HomeMy WebLinkAboutNC0021873_Permit (Issuance)_20130712NPDES DOCUMENT SCANNING: COVER !SHEET
NPDES Permit:
NC0021873
Mayodan WWTP
Document Type: ,
Permit Issuance
Wasteload Allocation
Authorization to Construct (AtC)
Permit Modification
Complete File - Historical
Engineering Alternatives (EAA)
Correspondence
Owner Name Change
Instream Assessment (67b)
Speculative Limits
Environmental Assessment (EA)
Document Date:
July 12, 2013
This document is pri'ited on reuse paper - igrzore any
content on the re -I erse side
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North Carolina Department of Environment and Natural Resources
Division of Water Quality
Pat McCrory Thomas A. Reeder John E. Skvarla, III
Govemor Acting Director Secretary
July 12, 2013
Michael M. Brandt
Town Manager
Town of Mayodan
210 W. Main Street
Mayodan, North Carolina 27027
Subject: Issuance of NPDES Permit Renewal
NC0021873
Town of Mayodan WWTP
Rockingham County
Dear Mr. Brandt:
The Division of Water Quality (Division) personnel have reviewed and approved your application for
renewal of the subject permit. Accordingly, we are forwarding the attached NPDES discharge permit. It
is issued pursuant to the requirements of North Carolina General Statute 143-215.1 and the Memorandum
of Agreement between North Carolina and the U.S. Environmental Protection Agency dated October 15,
2007, or as subsequently amended.
There are changes to this permit from the draft permit dated January 16, 2013:
(1) At the request of Ms. Nadine Blackwell of United Water, effluent data supplied has been reviewed
against the requirements for reducing sampling frequency for Exceptionally Performing Facilities. BOD,
TSS and Ammonia - N all met the requirements, so monitoring frequencies for these three parameters has
been reduced to 2/ Week for all flow regimes on Effluent Limitations and Monitoring Requirements
Sheets A.(1), A,(2), and A.(3). Fecal Coliform did not meet the requirements, so monitoring frequency
will remain the same as in your current permit.
(2) Special Condition A.(7.) has been revised and updated per the Division's Mercury Permitting
Strategy.
1617 Mail Service Center, Raleigh, North Carolina 27699-1617
Location: 512 N. Salisbury St. Raleigh, North Carolina 27604
Phone: 919-807-63001 FAX: 919-807-6492
Internet w►ww.ncwateroualitv.orq
None Carolina
XaturaIIji
An Equal opportunity 1 Affirmative Action Employer
i
The following changes have been made from the current permit:
• Add TRC footnote per permitting strategy.
• Revise annual effluent parameter scan to 3 scans per permit cycle during specified years in
accordance with revised EPA requirements.
• Adjust ammonia limits to not higher than 35 mg/ L.
• All monitoring requirements of the LTMP remain in place.
• A Total Mercury limit of 47 Ng/ L annual limit with Quarterly monitoring has been added to all 3
EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS pages, based on a
statistical review of your mercury discharge data from the DMR data, in keeping with the
Statewide Mercury TMDL and our TMDL implementation strategy; the old weekly average
mercury limit of 0.14 µg/ L on the 4.5 MGD sheet was removed.
• A Mercury Minimization Plan (MMP) has been added as Condition A.(7.) in accordance with the
recent mercury TMDL implementation strategy. The Mercury Minimization Plan must be
developed by January 28, 2014 and maintained at your facility.
• Sheet A.(1) - 2.5 MGD: Based on Reasonable Potential (to exceed Water Quality Standards)
Assessment (RPA) and our permitting strategy for metals, removed monitoring for Total Lead,
Total Selenium and Total Zinc, removed limits for Total Lead (Daily Max.) and Total Selenium
(Weekly Average and Daily Max.), changed to quarterly monitoring for Total Copper and Total
Silver and added quarterly monitoring for Total Chromium.
• Sheet A.(2) - 3.0 MGD: Based on Reasonable Potential (to. exceed Water Quality Standards)
Assessment (RPA) and our permitting strategy for metals, removed monitoring for Total Lead, Total
Selenium, and Total Zinc, removed limits for Total Lead (Daily Max.), and Total Selenium (both
Weekly Average and Daily Max.), changed to quarterly monitoring for Total Copper and Total
Silver and added Monthly Average and Daily Maximum limits with monthly monitoring for Total
Chromium.
• Sheet A.(3) - 4.5 MGD: Based on Reasonable Potential (to exceed Water Quality Standards)
Assessment (RPA) and our permitting strategy for metals, removed monitoring for Total Lead,
Total Selenium and Total Zinc, removed limits for Total Lead (Daily Max.), Total Mercury
(Weekly Average) and Total Selenium (both Weekly Average and Daily Max.), changed to
Quarterly monitoring for Total Copper and Total Silver and. added Monthly average and Daily
Maximum limits with monthly monitoring for Total Chromium.
We did receive comments from the North Carolina Wildlife Resources Commission. They are concerned
about chlorine and ammonia exposure to federal and state endangered James Spinymussel and Roanoke
Logperch, federal species of concern and state endangered Green Floater, state threatened Bigeye
Jumprock, state special concern Notched Rainbow and Riverweed Darter, and the state significantly rare
Roanoke Hogsucker. They requested, and DWQ strongly agrees, that you should consider converting to
an alternate disinfection agent, such as Ultra Violet light, to replace chlorine/ dechlorination. They also
requested site -specific Water Quality Standards for ammonia -nitrogen. A review of your DMRs shows
that you are doing a good job of controlling ammonia -nitrogen. We strongly encourage you to remain
vigilant regarding ammonia -nitrogen control. The ammonia -nitrogen limits will be reevaluated at the
next renewal.
If any parts, measurement frequencies, or sampling requirements contained in this permit are
unacceptable, you have the right to an adjudicatory hearing upon written request within thirty (30) days
after receiving this letter. Your request must take the form of a written petition conforming to Chapter
150B of the North Carolina General Statutes, and must be filed with the Office of Administrative
Hearings, 6714 Mail Service Center, Raleigh, North Carolina 27699-6714. Unless such demand is made,
this permit remains final and binding.
This permit is not transferable except after notifying the Division of Water Quality. The Division may
• modify and re -issue, or revoke this permit. Please notice that this permit does not affect your legal
obligation to obtain other permits required by the Division of Water Quality, the Division of Land
Resources, the Coastal Area Management Act, or other federal or local governments.
If you have questions, or if we can be of further service, please contact Jim McKay at
james.mckay@ncdenr.gov or call (919) 807-6404.
Sincerely,
ge Thomas A. Reeder
Enclosure: NPDES Peimmmit FINAL NC0021873 - Town of Mayodan WWTP
cc: Winston-Salem Regional Office, Surface Water Protection with Fact Sheet
EPA Region 4, Atlanta, with Fact Sheet - via email
NPDES Unit
Central Files
Monti Hassan, PERCS with Fact Sheet
Aquatic Toxicology, Susan Meadows - via email
NCWRC, Shari L. Bryant - via email
STATE OF NORTH CAROLINA .
DEPARTMENT OF ENVIRONMENT *AND NATURAL RESOURCES
DIVISION OF WATER QUALITY
PERMIT
TO DISCHARGE WASTEWATER UNDER THE
NATIONAL POLLUTANT DISCHARGE ELIMINATION SYSTEM
(NPDES)
In compliance with the provisions of North Carolina General Statute 143-215.1, other lawful standards and
regulations promulgated and adopted by the North Carolina Environmental Management Commission, and the
Federal Water Pollution Control Act, as amended, the
Town of Mayodan
is hereby authorized to discharge wastewater from a facility located at the
Mayodan WWTP
NC Highway 135 West, southeast of Mayodan
Rockingham County
to receiving waters designated as the Mayo River in the Roanoke River Basin in accordance with effluent
limitations, monitoring requirements, and other conditions set forth in Parts I, II, III and IV hereof.
The permit shall become effective August 1, 2013.
This permit and the authorization to discharge shall expire at midnight on May 31, 2017.
Signed this day July 12, 2013.
Thomas A. Reeder, Acting Director
/ Division of Water Quality
By Authority of the Environmental Management Commission
Permit NC0021873
3
SUPPLEMENT TO PERMIT COVER SHEET
All previous NPDES Permits issued to this facility, whether for operation or discharge are hereby revoked, and as of this
issuance, any previously issued permit bearing this number is no longer effective. Therefore, the exclusive authority to operate
and discharge from this facility arises under the permit conditions, requirements, terms, and provisions described herein.
The Town of .Mayodan is hereby authorized to:
1. Continue to operate an existing 4.5 MGD wastewater treatment facility that includes the following
wastewater treatment components:
■ Mechanical bar screen
• Dual path aeration basins
• Secondary clarifiers V
• Liquid Chlorination
■ Liquid Dechlorination
■ Effluent flow meter
• Sludge thickener �
• Aerobic digester
■ Backup generator/
This permitted facility is located off NC Highway 135 southeast of Mayodan in Rockingham County.
2. Continue to operate at 2.5 MGD wastewater treatment facility until the average flow for any calendar
year exceeds 80% of the permitted flow (2.0 MGD), after which time the facility must monitor in
accordance with effluent limitations and monitoring requirements specified for 3.0 MGD, and
3. Continue to operate at 3.0 MGD wastewater treatment facility until the average flow for any calendar
year exceeds 80% of the permitted flow (2.4 MGD), after which time the facility must monitor in
accordance with effluent limitations and monitoring requirements specified for 4.5 MGD, and
4. Discharge from said treatment works via Outfall 001 [specified on the attached map] into the Mayo
River, a Class C waterbody within the Roanoke River Basin.
Page 2 of 9
Permit NC0021873
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Facility
Town of Mayodan %TP
Latitude: 35 2f.25" N State CA&Ouad: B19 NW/Mayada:; NC
LocationAllidlifF)
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Loot hales 77 57'S6" W Permitted Flow; 25/3.CV4SMGD
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NPDES Permit No, NC0021873
: C Sub -Basin' 03-02-02
Stream Class:
Rockingham County
PatrP of Q
Permit NC0021873
A. (1.) EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS (2.5 MGD)
Beginning on the permit effective date and lasting until the twelve (12) month average flow for any calendar year
exceeds- 2.0 MGD, or until permit expiration, the Permittee is authorized to discharge treated wastewater from
Outfall 001. Such discharges shall be limited and monitored by the Permittee as specified below:
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Flow
2.5 MGD
Continuous
Recording
Influent or Effluent
BOD, 5-day, 20°C 1
30.0 mg/L
45.0 mg/L
2/Week
Composite
Influent and Effluent
Total Suspended Solids 1
30.0 mg/L
45.0 mg/L
2/Week
Composite
Influent and Effluent
NH3 as N (Apr 1 - Oct 31) '
16.0 mg/L
35.0 mg/L
•
2/Week
Composite
Effluent
NH3 as N (Nov 1- Mar 31)
Weekly
Composite
Effluent
Total Residual Chlorine 2
28 µg/L
3/Week
Grab
Effluent
Fecal Coliform
(geometric mean)
200/100 ml
400/100 ml
3/Week
Grab
Effluent
pH
> 6.0 and < 9.0 standard units
3/Week
Grab
Effluent, Up, Down 3
Dissolved Oxygen
3/Week
Grab
Effluent, Up, Down 3
Temperature
3/Week
Grab
Effluent, Up, Down 3
Conductivity
3/Week
Grab
Effluent, Up, Down 3
Total Nitrogen
(NO2+NO3+TKN)
Monthly
Composite
Effluent
Total Phosphorus
Monthly
Composite
Effluent
Total Chromium
Quarterly 5
Composite
Effluent
Total Mercury 4
47 ng/ L Annual Average
Quarterly
Grab
Effluent
Total Silver
Quarterly 5
Composite
Effluent
Total Copper
Quarterly. 5
Composite
Effluent
Chronic Toxicity 6
Quarterly
Composite
Effluent
Effluent Pollutant Scan
Monitor and Report
Footnote 7
Footnote 7
Effluent
Notes:
1.
The monthly average effluent BODS and TSS concentrations shall not exceed 15% of the respective influent value
(i.e., 85% removal is required).
2. Limit and monitoring apply only if chlorine or chlorine derivatives are used for disinfection. The Division shall
consider all effluent TRC values reported below 50 µg/L to be in compliance with the permit. However, the
Permittee shall record and submit all values reported by a North Carolina certified laboratory (including field
certified), even if these values fall below 50 µg/L.
3. See Part A. (6.) for instream sampling requirements.
4. Mercury sampling and analyses shall be conducted using techniques described in USEPA test Method 1631E.
5. Sample in conjunction with Quarterly Toxicity Test.
6. Chronic Toxicity (Ceriodaphnia) at 5 % with testing in March, June, September and December [see A. (4.)].
7. The permittee shall perform three Effluent Pollutant Scans during the term of this permit [see A. (5.)].
The Permittee shall discharge no floating solids or foam visible in other than trace amounts.
Page 4 of 9
Permit NC0021873
0
A. (2.) EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS (3.0 MGD)
During the period after the twelve (12) month average flow exceeds 2.0 MGD and lasting until the twelve (12)
month average flow for any calendar year exceeds 2.4 MGD, or until permit expiration, the Permittee is
authorized to discharge from Outfall 001. Such discharges shall be limited and monitored by the Permittee as
specified below:
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Flow
3.0 MGD
Continuous
Recording
Influent or Effluent
BOD, 5-day, 20°C 1 .
30.0 mg/L
45.0 mg/L
2/Week
Composite
Influent and Effluent
Total Suspended Solids'
30.0 mg/L
45.0 mg/L
2/Week
Composite
Influent and Effluent
NH3 as N (Apr 1 - Oct 31)
14.0 mg/L
35.0 mg/L
2/Week
Composite
Effluent
NH3 as N (Nov 1— Mar 31)
Weekly
Composite
Effluent
Total Residual Chlorine 2
28 µg/L
Daily
Grab
Effluent
Fecal Coliform •
(geometric mean)
200/100 ml
400/100 ml
Daily
Grab
Effluent
pH
> 6.0 and < 9.0 standard units
Daily
Grab
Effluent, Up, Down 3
Dissolved Oxygen
Daily
Grab
Effluent, Up, Down 3
Temperature
Daily
Grab
Effluent, Up, Down 3
Conductivity
Daily
Grab
Effluent, Up, Down 3
Total Nitrogen
(NO2+NO3+11(N)
Monthly
Composite
Effluent
Total Phosphorus
Monthly
Composite
Effluent
Total Chromium
856 µg/L
14,500 µg/L
Monthly 5
Composite
Effluent
Total Mercury 4
47 ng/ L Annual Average
Quarterly
Grab
Effluent
Total Silver
Quarterly 5
Composite
Effluent
Total Copper
Quarterly 5
Composite
Effluent
Chronic Toxicity 6
Quarterly
Composite
Effluent
Effluent Pollutant Scan
Monitor and Report
Footnote 7
Footnote 7
Effluent
Notes:
1. The monthly average effluent BOD5 and TSS concentrations shall not exceed 15% of the respective influent value (i.e.,
85% removal is required).
2. Limit and monitoring apply only if chlorine or chlorine derivatives are used for disinfection. The Division shall consider
all effluent TRC values reported below 50 µg/L to be in compliance with the permit. However, the Permittee shall record
and submit all values reported by a North Carolina certified laboratory (including field certified), even if these values fall
below 50 µg/L.
3. See Part A. (6.) for instream sampling requirements.
4. Mercury sampling and analyses shall be conducted using techniques described in USEPA test Method 1631E.
5. Sample in conjunction with Quarterly Toxicity Test.
6. Chronic Toxicity (Ceriodaphnia) at 6% with testing in March, June, September and December [see A. (4.)].
7. The permittee shall perform three Effluent Pollutant Scans during the term of this permit [see A. (5.)].
The Permittee shall discharge no floating solids or foam visible in other than trace amounts.
Page 5 of 9
Permit NC0021873
A. (3.) EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS (4.5 MGD)
During the period after the twelve (12) month average flow for any calendar year exceeds 3.0 MGD, and
lasting until permit expiration, the Permittee is authorized to discharge from Outfall 001. Such discharges shall
be l;m;+ed and monitored by the Permittee as specified below.
LIIVIITATIONS_ ...
, _ :1V ONTTORIngy EQUIREMENTS
} _.-
;EFFLUENT
PARAMETER
F �;z =Y -
onfhlyr
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1
.
Flow
4.5 MGD
Continuous
Recording
Influent or Effluent
BOD, 5-day, 20°C 1
30.0 mg/L
45.0 mg/L
2/Week
Composite
Influent and Effluent
Total Suspended Solids 1
30.0 mg/L
45.0 mg/L
2/Week
Composite
Influent and Effluent
NH3 as N (Apr 1- Oct 31)
9.0 mg/L
27.0 mg/L
2/Week
Composite
Effluent
NH3 as N (Nov 1 - Mar 31)
31.5 mg/L
35.0 mg/L
2/Week
Composite
Effluent
Total Residual Chlorine 2
28 µg/L
Daily
Grab
Effluent
Fecal Coliform
(geometric mean)
200/100 ml
400/100 ml
Daily
Grab
Effluent
pH 1/
> 6.0 and < 9.0 standard units
Daily
Grab
Effluent, Up, Down 3
Dissolved Oxygen , ;
•
Daily
Grab
Effluent, Up, Down 3
Temperature ) ` -
Daily
Grab
Effluent, Up, Down 3
Conductivity i
Daily
Grab
Effluent, Up, Down 3
Total Nitrogen
(NO2+NO3+TKN)
Monthly
Composite
Effluent
Total Phosphorus
Monthly
Composite
Effluent
Total Chromium
587 µg/L
10,000 µg/L
Monthly 5
Composite
Effluent
Total Mercury 4
47 ng/ L Annual Average
Quarterly
Grab
Effluent
Total Silver
Quarterly 5
Composite
Effluent
Total Copper
Quarterly 5
Composite
Effluent
Chronic Toxicity 6
Quarterly
Composite
Effluent
Effluent Pollutant Scan
Monitor and Report
Footnote 7
Footnote 7
Effluent
Notes:
1. The monthly average effluent BODS and TSS concentrations shall not exceed 15% of the respective influent value
(i.e., 85% removal is required).
2. Limit and monitoring apply only if chlorine or chlorine derivatives are used for disinfection. The Division shall
consider all effluent TRC values reported below 50 µg/L to be in compliance with the permit. However, the Permittee
shall record and submit all values reported by a North Carolina certified laboratory (including field certified), even if
these values fall below 50 µg/L.
3. See Part A. (6.) for instream sampling requirements.
4. Mercury sampling and analyses shall be conducted using techniques described in USEPA test Method 1631 E.
5. Sample in conjunction with Quarterly Toxicity Test.
6. Chronic Toxicity (Ceriodaphnia) at 9 % with testing in March, June, September and December [see A. (4.)].
7. The permittee shall perform three Effluent Pollutant Scans during the term of this permit [see A. (5)]
The Permittee shall discharge no floating solids or foam visible in other than trace amounts.
Page 6 of 9
Permit NC0021873
• A. (4.) QUARTERLY CHRONIC TOXICITY PERMIT LIMIT, ALL FLOW REGIMES
The effluent discharge shall at no time exhibit observable inhibition of reproduction or significant mortality to Ceriodaphnia
dubia at an effluent concentration of 5% at 2.5 MGD flow regime, 6% at 3.0 MGD flow regime, and 9% at 4.5 MGD flow
regime.
The permit holder shall perform at a minimum, quarterly monitoring using test procedures outlined in the "North Carolina
Ceriodaphnia Chronic Effluent Bioassay Procedure," Revised December 2010, or subsequent versions or "North Carolina
Phase II Chronic Whole Effluent Toxicity Test Procedure" (Revised- December 2010) or subsequent versions. The tests will
be performed during the months of March, June, September and December. These months signify the first month of each
three month toxicity testing quarter assigned to the facility. Effluent sampling for this testing must be obtained during
representative effluent discharge and shall be performed at the NPDES permitted fmal effluent discharge below all treatment
processes.
If the test procedure performed as the first test of any single quarter results in a failure or ChV below the permit
limit, then multiple -concentration testing shall be performed at a minimum, in each of the two following months as
described in "North Carolina Phase II Chronic Whole Effluent Toxicity Test Procedure" (Revised -December 2010) or
subsequent versions.
All toxicity testing results required as part of this permit condition will be entered on the Effluent Discharge Monitoring Form
(MR-1) for the months in which tests were performed, using the parameter code TGP3B for the pass/fail results and THP3B
for the Chronic Value. Additionally, DWQ Form AT-3 (original) is to be sent to the following address:
Attention: North Carolina Division of Water Quality
Environmental Sciences Section
1621 Mail Service Center
Raleigh, North Carolina 27699-1621
Completed Aquatic Toxicity Test Forms shall be filed with the Environmental Sciences Section no later than 30 days after the
end of the reporting period for which the report is made.
Test data shall be complete, accurate, include all supporting chemical/physical measurements and all concentration/response
data, and be certified by laboratory supervisor and ORC or approved designate signature. Total residual chlorine of the
effluent toxicity sample must be measured and reported if chlorine is employed for disinfection of the waste stream.
Should there be no discharge of flow from the facility during a month in which toxicity monitoring is required, the permittee
will complete the information located at the top of the aquatic toxicity (AT) test form indicating the facility name, permit
number, pipe number, county, and the month/year of the report with the notation of "No Flow" in the comment area of the
form. The report shall be submitted to the Environmental Sciences Section at the address cited above.
Should the permittee fail to monitor during a month in which toxicity monitoring is required, monitoring will be required
during the following month. Assessment of toxicity compliance is based on the toxicity testing quarter, which is the three
month time interval that begins on the first day of the month in which toxicity testing is required by this permit and continues
until the final day of the third month.
Should any test data from this monitoring requirement or tests performed by the North Carolina Division of Water Quality
indicate potential impacts to the receiving stream, this permit may be re -opened and modified to include alternate monitoring
requirements or limits.
If the Permittee monitors any pollutant more frequently than required by this permit, the results of such monitoring shall be
included in the calculation & reporting of the data submitted on the DMR & all AT Form submitted.
NOTE: Failure to achieve test conditions as specified in the cited document, such as minimum control organism survival,
minimum control organism reproduction, and appropriate environmental controls, shall constitute an invalid test and will
require immediate follow-up testing to be completed no later than the last day of the month following the month of the initial
monitoring.
Page 7 of 9
Permit NC0021873 -
4.
A. (5.) EFFLUENT POLLUTANT SCAN
The Permittee shall perform a total of three (3) Effluent Pollutant Scans for all parameters listed below. One
scan must be performed in each of the following years: 2014, 2015, and 2016. Analytical methods shall be in
accordance with 40 CFR Part 136 and shall be sufficiently sensitive to determine whether parameters are
present in concentrations greater than applicable standards and criteria. Samples should be collected with one
quarterly toxicitytest each year, and must represent seasonal variation [i.e., do not sample in the same quarter
every year]. Unless otherwise indicated, metals shall be analyzed as "total recoverable."
Ammonia (as N)
Chlorine (total residual, TRC)
Dissolved oxygen
Nitrate/Nitrite
Kjeldalil nitrogen
Oil and grease
Phosphorus
Total dissolved solids
Hardness
Antimony
Arsenic
Beryllium
Cadmium
Chromium
Copper
Lead
Mercury (EPA Method 1631E)
Nickel
Selenium
Silver
Thallium
Zinc
Cyanide
Total phenolic compounds
Volatile organic compounds:
Acrolein
Acrylonitrile
Benzene
Bromoform
Carbon tetrachloride
Chlorobenzene
Chlorodibromomethane
Chloroethane
2-chloroethylvinyl ether
Chloroform
Dichlorobromomethane
1,1-dichloroethane
1,2-dichloroethane
Trans-1,2-dichloroethylene
1,1-dichloroethylene
1,2-dichloropropane
1,3-dichloropropylene
Ethylbenzene
Methyl bromide
Methyl chloride
Methylene chloride
1,1,2,2-tetrachloroethane
Tetrachloroethylene
Toluene
1,1,1-trichloroethane
1,1,2-trichloroethane
Trichloroethylene
Vinyl chloride
Acid -extractable compounds:
P-chloro-m-cresol
2-chlorophenol
2,4-dichlorophenol
2,4-dimethylphenol
4,6-dinitro-o-cresol
2,4-dinitrophenol
2-nitrophenol
4-nitrophenol
Pentachlorophenol
Phenol
2,4,6-trichlorophenol
Base -neutral compounds:
Acenaphthene
Acenaphthylene
Anthracene
Benzidine •
Benzo(a)anthracene
Benzo(a)pyrene
3,4 benzofluoranthene
Benzo(ghi)perylene
Benzo(k)fluoranthene
Bis (2-chloroethoxy) methane
Bis (2-chloroethyl) ether
Bis (2-chloroisopropyl) ether
Bis (2-ethylhexyl) phthalate
4-bromophenyl phenyl ether
Butyl benzyl phthalate
2-chloronaphthalene
4-chlorophenyl phenyl ether
Chrysene
Di-n-butyl phthalate
Di-n-octyl phthalate
Dibenzo(a,h)anthracene
1,2-dichlorobenzene
1,3-dichlorobenzene
1,4-dichlorobenzene
3,3-dichlorobenzidine
Diethyl phthalate
Dimethyl phthalate
2,4-dinitrotoluene
2,6-dinitrotoluene
1,2-diphenylhydrazine
Fluoranthene
Fluorene
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclo-pentadiene
Hexachloroethane
Indeno (1, 2, 3-cd)pyrene
Isophorone
Naphthalene
Nitrobenzene
N-nitrosodi-n-propylamine
N-nitrosod methylamine
N-nitrosodiphenylamine
Phenanthrene
Pyrene
1,2,4-trichlorobenzene
Reporting. Test results shall be reported on DWQ Form -A MR PPA1 (or in a form approved by the Director) by
December 30 of each designated sampling year: The report shall be submitted to the following address: NC
DENR / DWQ / Central Files, 1617 Mail Service Center, Raleigh, North Carolina 27699-1617.
Page 8 of 9
Permit NC0021873
A. (6.) INSTREAM MONITORING REQUIREMENTS
Parameter
Monitoring Requirements
Measurement Frequency
Sample Type
Sample Location
Dissolved Oxygen
June -September
3/week
Grab
Upstream at NC Hwy 135,
Downstream at NCSR 2177
October -May
1/week
Temperature
June -September
3/week
Grab
Upstream at NC Hwy 135,
Downstream at NCSR 2177
October -May
1/week
pH
June -September
3/week
Grab
Upstream at NC Hwy 135,
Downstream at NCSR 2177
October -May
1/week
Conductivity
June -September
3/week
Grab
Upstream at NC Hwy 135,
Downstream at NCSR 2177
1/week
A.(7.) MERCURY MINIMIZATION PLAN (MMP).
Mercury Minimization Plan (MMP). The permittee shall develop and implement a mercury
minimization plan during this permit term. The MMP shall be developed by January 28, 2014 (180 days
from the NPDES Permit Effective Date), and shall be available for inspection on -site. A sample MMP
was developed through a stakeholder review process and has been placed on the Division website for
guidance (http://portal.ncdenr.org/web/wq/swp/ps/npdes), under Model Mercury Minimization Plan.
The MMP should place emphasis on identification of mercury contributors and goals for reduction.
Results shall be summarized and submitted with the next permit renewal.
Page 9 of 9
Avral
NCDENR
North Carolina Department of Environment and Natural Resources
Division of Water Quality
Pat McCrory Thomas A. Reeder John E. Skvarla, III
Governor Acting Director Secretary
June 24, 2013
Shari L. Bryant
Piedmont Region Coordinator
Habitat Conservation Program
NC Wildlife Resources Commission
1721 Mail Service Center
Raleigh, NC 27699-1721
Subject: Review comments
NPDES Permit NC0021873
Mayodan Wastewater Treatment Plant
Rockingham County
Dear Ms. Bryant:
Thank you for your review of the draft renewal of NPDES Permit NC0021873 for the Mayodan
Wastewater Treatment Plant in Rockingham County. In the review, you made two requests for
changes, based on the presence of rare, threatened and endangered aquatic life species:
1. To encourage the Permittec to switch to an alternate disinfection media from chlorine, and,
2. To develop site specific ammonia limits in order to better protect sensitive rare, threatened
and protected mussels and other aquatic life.
(1.) We have no mechanism for requiring disinfection with alternatives to chlorination as long as
the permittee is in compliance with permit limits and is not expanding the plant capacity or
changing the treatment. A review of Discharge Monitoring Reports for 2010 through October,
2012 shows all samples were below detection levels at less than 10 µg/ L. The facility conducts
regular quarterly Whole Effluent Toxicity Tests in accordance with EPA and NC requirements at
the IWC concentration. They failed one test in April 2000, but have passed all subsequent tests
(over 52 consecutive tests). I will add language to the Cover Letter to the final permit to inform
the permittee of this concern, and strongly recommend that he investigates converting to UV
disinfection from chlorination/ dechlorination.
1617 Mail Service Center, Raleigh, North Carolina 27699-1617
Location: 512 N. Salisbury St. Raleigh, North Carolina 27604
Phone: 919.807-63001 FAX: 919-807-64989
Internet: www.ncwateraualitv.orq
An Equal opportunity l Affirmative Action Employer
NorthCarolina
atura!!ji
(2.) The plant is currently meeting all ammonia - nitrogen water quality limits. I have calculated
the in -stream ammonia concentration using DMR data for effluent flow and ammonia - N
concentration and conservative 7Q10 flows for the Mayo river at the discharge site. The
Division uses 0.22 mg/ L as the normal background ammonia concentration for evaluations. The
resulting calculated in -stream concentrations were generally the same or slightly higher than the
background ammonia-N concentrations (0.22 to 0.25 mg/ L), allowing for 7Q10 dilution. The
highest instream concentration was 0.45 mg/ L in May 2010. See attached Ammonia-N
predicted lnstream Concentrations, Mayo WWTP 2010 - October 2012. Again, language will be
added to the permit cover letter addressing the concerns about ammonia and sensitive aquatic
life, encouraging the facility to continue addressing ammonia discharges.
Thank you again for your review.
Sincerely,
p:„.„..,
/r c /
Jim McKay
Complex NPDES Permitting
NC0021873
Ammonia-N predicted Instream Concentrations, Mavo WWTP 2010 - October 2012
Based on DMR Data and 7Q10 Flows
Monthly Calculated
Avg. Monthly Avg. Ammonia-N Ammonia-N Ammonia-N
Monthly Avg. Effluent Effluent In -Stream In -Stream Discharge Limit,
Effluent Flow Flow Ammonia-N 7Q10 Concentration Standard (Monthly Avg.)
Date MGD cfs mg/ L cfs mg/ L mg/ L mg/ L
Jan-10 1.487 2.30 1.12 131 0.24 1.8
Feb-10 1.792 2.78 0.51 131 0.23 1.8
Mar-10 1.368 2.12 0.60 131 0.23 1.8
Apr-10 1.063 1.65 4.50 75 0.31 1.0 16
May-10 0.803 1.24 14.35 75 0.4S 1.0 16
Jun-10 0.724 1.12 10.47 75 0.37 1.0 16
Jul-10 0.751 1.16 0.28 75 0.22 1.0 16
Aug-10 0.959 1.49 0.23 75 0.22 1.0 16
Sep-10 0.848 1.31 0.71 75 0.23 1.0 16
Oct-10 1.216 1.88 1.31 75 0.25 1.0 16
Nov-10 0.898 1.39 0.51 131 0.22 1.8
Dec-10 1.04 1.61 1.34 131 0.23 1.8
Jan-11 0.884 1.37 1.22 131 0.23 1.8
Feb-11 0.847 1.31 0.23 131 0.22 1.8
Mar-11 1.393 2.16 1.41 131 0.24 1.8
Apr-11 1.108 1.72 1.98 75 0.26 1.0 16
May-11 1.092 1.69 1.35 75 0.24 1.0 16
Jun-11 0.797 1.24 0.30 75 0.22 1.0 16
Jul-11 0.722 1.12 0.22 75 0.22 1.0 16
Aug-11 0.702 1.09 0.77 75 0.23 1.0 16
Sep-11 0.776 1.20 1.96 75 0.25 1.0 16
Oct-11 0.786 1.22 0.32 75 0.22 1.0 16
Nov-11 0.98 1.52 2.28 131 0.24 1.8
Dec-11 0.91 1.41 0.86 131 0.23 1.8
Jan-12 0.911 1.41 0.11 131 0.22 1.8
Feb-12 0.787 1.22 0.83 131 0.23 1.8
Mar-12 1.181 1.83 0.30 131 0.22 1.8
Apr-12 0.921 1.43 1.32 75 0.24 1.0 16
May-12 0.811 1.26 0.50 75 0.22 1.0 16
Jun-12 0.653 1.01 0.34 75 0.22 1.0 16
JuI-12 0.66 1.02 0.36 75 0.22 1.0 16
Aug-12 0.794 1.23 1.04 75 0.23 1.0 16
Sep-12 0.753 1.17 0.23 75 0.22 1.0 16
Oct-12 0.758 1.17 1.11 75 0.23 1.0 16
0.24
Average
0.45
Maximum
0.22
Minimum
40
30
J
E 20
MAYODAN WWTP
Monthly BOD
10—
0 I I I I I
O O O
T T T
L
as
oTs
O
T
O
0
Z
�
Q
CO
T
0
Z
Date (1/1/2010 to 12/31/2012 )
/ Effluent BOD mg/L (Mo Avg)
N
cca
I IIIIII
N N N CO
T T T T
Cr)- as o as
Z
W/MS (NC MAYODAN WWTP)
Effluent BOD Monthly
MoMaxLimit
I
50
40
30
MAYODAN WWTP
Weekly BOD
20-
10
A
1
1
I 00
Ao
joAl\,,-
1/3/10 4/11/10 7/18/10 10/24/10 1/30/11 5/8/11 8/14/11 11/20/11 2/26/12 6/3/12
0 I 1
i\rW\,
I
A
I
I
I
I
I
Week Ending Dates (1/1/2010 to 12/31/2012 )
/ Effluent BOD mg/L (Wk Avg)
I
I
WklyMaxLimit
9/9/12 12/16/12 3/24/13
WIM5 (NC MAYODAN WWTP)
Effluent SOD Weekly
40
30
MAYODAN WWTP
Monthly TSS
-J
E 20-
10
0 0 0 0 0 0 r
✓ r r r r r r r
C L. >+ = n > c
Bg � - v) Z - 2
as
r
0_
0
z
Date (1 /1 /2010 to 12/31 /2012 )
/ Effluent TSS mg/L (Mo Avg)
r
C0
{
N
CB
N_
N
C2
a)
{
W1MS (NC MAYODAN WWTP)
Effluent BOD Monthly
MoMaxLimit
100
80
60-
40
MAYODAN WWTP
Weekly TSS
20—
L
vi\,"/
r
i
0 l l i i � l„
1/3/10 4/11/10 7/18/10 10/24/10 1/30/11 5/8/11 8/14/11 11/20/11 2/26/12 6/3/12 9/9/12 12/16/12 3/24/13
WklyMaxLimit
Week Ending Dates (1/1/2010 to 12/31/2012 )
/ Effluent TSS mg/L (Wk Avg)
W1MS (NC MAYODAN WWTP)
Effluent TSS Weekly
15
0
T T
0
MAYODAN UVWTP
Monthly Ammonia
T T T T T T T T
L o^+ L
W 0 CIS CC1
-, 2 M CO Z - 2
Date (1 /1 /2010 to 12/31 /2012 )
/ Effluent NH3 N mg/L (Mo Avg)
WIMS (NC MAYODAN WWTP)
Effluent Ammonia Monthly
25
20--
15--
J
as
E
10
5
0
1
r
MAYODAN WWTP
Weekly Ammonia
I
1
I
1
1
1
U I rll....._ `_+__.` ll.,,r. ILIA
1/3/10 4/11/10 7/18/10 10/24/10 1/30/11 5/8/11 8/14/11 11/20/11 2/26/12 6/3/12 9/9/12 12/16/12 3/24/13
Week Ending Dates (1/1/2010 to 12/31/2012 )
/ Effluent NH3 N mg/L (Wk Avg)
WIMS (NC MAYODAN WWTP)
Effluent Ammonia Weekly
250—T
200
150
MAYODAN WVVTP
Monthly Fecal Coliform
Date (1 /1 /2010 to 12/31 /2012 )
/ Effluent Fecal #/100 Mo (Mo Avg)
WIMS (NC MAYODAN WWTP)
Effluent BOD Monthly
MoMaxLimit
MAYODAN 1NV TP
Weekly Fecal Coliform
1
1
j I "� -mot
Week Ending Dates (1/1/2010 to 12/31/2012 )
/ Effluent Fecal #/100 We (Wk Avg)
W/MS (NC MAYODAN WWTP)
Effluent Fecal Coliform Weekly
WklyMaxL
DENR/DWQ
Table 1
FACT SHEET
FOR NPDES PERMIT DEVELOPMENT
NPDES NC0021873
Facility Sum mary
General Information
Applicant/Facility Name:
Town of Mayodan WWTP
Applicant Address:
210 W. Main Street, Mayodan, NC 27027
Facility Address:
293 Caldwell Road, Mayodan, NC 27027
Permitted Flow (Compliance
keyed on 80 % of tiered flow)
2.5 MGD (existing)
3.0 MGD (existing)
4.5 MGD (existing)
Type of Waste:
Domestic and Industrial
Facility Classification:
Class III (2.5 MGD), Class IV (3.0 & 4.5 MGD)
Permit Status:
Renewal
County:
Rockingham
Discharge Location and Conditions
Receiving Stream:
Mayo River
Regional Office:
W-SRO
Stream Classification:
C
State Grid:
B 19 NW
303(d) Listed?
Not on 2012
Approved list.
USGS Quad:
Mayodan, NC
Basin:
Roanoke
Permit Writer:
Jim McKay
Subbasin:
03 02 02
HUC:
0301010304
Date:
June 28, 2013
Drainage Area (mi2)
312
(Not To Scale)
Lat. 36° 24' 25" N Long. 79° 57' 56" W
Summer 7Q10 (cfs)
75
Winter 7Q10 (cfs):
131
30Q2 (cfs)
150:.
Average Flow (cfs)
362
I WC (%)
5 % (2.5MGD)
6 % (3.0 MGD)
9% (4.5 MGD)
Introduction
The Town of Mayodan Wastewater Treatment Plant (WWTP), herein called Mayodan or the Permittee,
requires a National Pollutant Discharge Elimination System (NPDES) permit to dispose treated wastewater to
the surface waters of the state. The Permittee's 5-year NPDES permit expired May 31, 2012 and they have
requested renewal from the Division of Water Quality (the Division). This Fact Sheet summarizes background
information and rationale used by the Division's NPDES Unit to determine permit limits and monitoring
conditions.
Existing Treatment System: As a regional facility, Mayodan services 2,505 local residents plus industry, and
receives industrial and domestic influent flow from the towns of Stoneville (1,118 residents) and Madison
(2,423 residents). In 2002 the Town applied for expansion from 3.0 MGD to 4.5 MGD in order to add service
to Stoneville and Madison. In 2007, as a result of loss of a major SIU, the Town applied for a flow reduction
modification to the permit in order to downgrade to 2.5 MGD, thereby going from a Class IV to a Class III
facility with corresponding relaxed limits and monitoring conditions. The average discharge for the period of
2010 through October 2012 is 0.946 MGD.
Fact Sheet
NPDES NC0021873
Renewal
Page 1
Permittee's Renewal Application: The current permit expired on May 31, 2012. The Division received the
Permittee's request to renew the permit (EPA Form 2A) on December 19, 2011.
Regional Office Report: Winston-Salem Regional Office (W-SRO) inspector Aana Taylor -Smith conducted an
annual facility inspection on April 17, 2013. The facility was found to be in good condition and well maintained.
A couple of minor problems were identified: the sample tubing for the influent composite sampler needed to be
replaced, and there was a screw loose on one of the secondary clarifier skimmer arms, causing it to be tilted. Both
were corrected by the facility.
Waste Load Allocation (WLA): The Division prepared the last WLA in 2007 for the receiving stream and
developed effluent limits and monitoring requirements considering an in -stream waste concentration (IWC) of
4.91 % (2.5 MGD), 5.84 % (at 3.0 MGD), and 8.51 % (at 4.5 MGD). These IWCs have been rounded up to 5%,
6% and 9%, respectively for Whole Effluent Toxicity testing. The Division views the limits and monitoring
requirements appropriate for renewal except as outlined below (see Renewal Summary).
Existing Stream Conditions: The Permittee discharges to the Mayo River [Stream Index 22-30-(10)]; this
segment is a Class C waterbody within the Roanoke River Basin. The Mayo River is not listed on North
Carolina's 303d list of impaired waters (Final 2012). The Mayo River is classified as Good for benthic
microinvertebrates near the NC -VA border and is classified as Good -Fair downstream of the discharge at the
confluence with the Dan River.
Pre-treatment: Mayodan has an approved Pretreatment Program under federal and state regulations (40CFR
403 and NC State 15A NCAC 2H.0900), and this program will continue with renewal. Mayodan is a regional
WWTP serving the towns of Mayodan, Stoneville, and Madison. Mayodan regulates all Significant Industrial
Users (SIUs) in its service area, currently totaling two SIUs: Unifi Sans, which produces spun nylon fiber,
permitted flow is 0.0234 MGD; and Unifi 105, which produces textured and covered nylon fiber, permitted
flow is 0.103 MGD. Neither is categorical.
DMR Effluent Data Review: Mayodan's monthly Discharge Monitoring Reports (DMRs) appear regular,
thorough, and complete. The Division compared effluent flow rates from January 2010 through March 2012. The
Division also evaluated data for metals and toxicants during the same time period (see Reasonable Potential
Analysis).
Whole Effluent Toxicity: The permit has a requirement for a quarterly chronic toxicity test at 5 % at 2.5 MGD
flow regime using ceriodaphnia. The Division reviewed Mayodan's quarterly Whole Effluent Toxicity records
from January 2008 through December 2012 (20 quarterly tests). Mayodan passed all toxicity testing during this
5-year period. The Permittee also conducted second -species WET testing during the months of April 2011, July
2011, and September 2011. All test results were reported as "pass."
Instream Monitoring: The current permit requires monitoring in -stream for pH, Temperature, D.O. and
conductivity. A review of DMR data from 2010 through 2012 shows very little difference between upstream and
downstream data. In general, pH downstream was 0.1 to 0.2 S.U. lower than upstream, Temperature downstream
was within 1 degree C of upstream, D.O. downstream was within 0.1 to 0.2 mg/ L of upstream, and conductivity
downstream was within 1 to 2 µmhos/ cm of the upstream value. All conductivity values upstream and down are
in the 60 to 70 µmhos/ cm range. This is expected due to the large dilution in the Mayo River. At 2.5 MGD the
IWC is 4.9%; at the 3 year average flow of 0.946 mgd and 7Q10 flow, IWC is 1.9%.
Recommendation: Retain current in -stream monitoring program. Conductivity monitoring is maintained due to
industrial contributions to the WWTP.
Fact Sheet
NPDES NC0021873
Renewal
Page 2
PERMIT RENEWAL
Chronic Reasonable Potential Analysis (RPA): In order to establish a list of Pollutants Of Concern (POCs),
the Division examined the permit application, pretreatment data, DMRs (2010 through March 2012), and the
Basin Plan. The Division conducted RPA for each proposed flow of 2.5 MGD, 3.0 MGD and 4.5 MGD, using
7Q10 dilution, to calculate a maximum predicted concentration for each POC (see attached RPA Summary
sheets). Each maximum was then compared to the POC's freshwater Standard or allowable concentration
(Tables 2, 3, and 4). If by this method, a POC showed reasonable potential (RP) to exceed its Standard or
criteria, the Division included a permit limit as a Monthly Average to protect against chronic toxicity impacts.
Acute RPA: Similar to the Chronic RPA, the Division compared each POC's maximum predicted concentration
to the freshwater Final Acute Value ('/2 FAV) or EPA Criteria Maximum Concentration (CMC) to establish the
potential for acute toxicity (Tables 2, 3, and 4). The acute RPA uses 1 Q 10 dilution. If by this method, a POC
showed reasonable potential to exceed its freshwater 1/2 FAV/CMC, the Division included this allowable
concentration as a permit limit Daily Maximum to protect the receiving stream against acute toxic affects.
Table 2
RPA - 2.5 MGD
Parameter
Chronic
Allowable
OWL)
Acute
Allowable
(t )
Maximum
Predicted
(!�)
RP
�
Comments
Arsenic AL
1,018.3
N/A
7.9
N
Monitored by LTMP only.
Arsenic HH
943.4
N/A
7.9
N
Monitored by LTMP only.
Cadmium
40.7
252.5
12.3
N
Monitored by LTMP only.
Chromium
1,018.3
17,205.4
886
N
Add Quarterly monitoring only.
Copper
142
122.9
107
N
Action Level parameter — no apparent
toxicity, change monitoring to Quarterly
from 2/ Month.
Cyanide
102
370.4
15.8
N
Monitored by LTMP only.
Lead
509
569
6.6
N
Remove limit and monitoring from
permit. Continue monitoring on LTMP.
Mercury
12 ng/ L
N/A
729.6 ng/L
Y
Add new 47 ng/ L Annual Average Limit
with Quarterly monitoring, per Statewide
TMDL.
Nickel
1,791
4,393.9
15.8
N
Not detected in 9 samples. Monitored
by LTMP only.
Selenium
102
942.8
5.0
N
Remove limit and monitoring from
permit. Continue monitoring on LTMP.
Silver
1.2
20.7
3.025
Y
Action Level parameter — no apparent
toxicity, change monitoring to Quarterly
from 2/ Month.
Zinc
1,018
1,127.9
283.4
N
Action Level parameter — no apparent
toxicity. Remove monitoring from
permit.
Fact Sheet
NPDES NC0021873
Renewal
Page 3
RPA-3.0 MGD
Parameter
Chronic
Allowable
OWL)
Acute
Allowable
(µlfL)
Maximum
Predicted
(llL)
RP
Comments
Arsenic AL
856.2
N/A
7.9
N
Monitored by LTMP only.
Arsenic HH
787.4
N/A
7.9
N
Monitored by LTMP only.
Cadmium
34
15
7
N
Monitored by LTMP only.
Chromium
856
14,496
886
Y
Add Limits and Monthly Monitoring
Copper
120
103.5
107
Y
Action Level parameter — no apparent
toxicity, change monitoring to Quarterly
from 2/ Month.
Cyanide
86
312
15.8
N
Monitored by LIMP only.
Lead
428
479.4
6.6
N
Remove limit and monitoring from
permit.
Mercury
206 ng/L
N/A
729.6 ng/L
Y
Add 47 ng/ L Annual Average Limit
with Quarterly monitoring, per Statewide
TMDL.
Nickel
1,507
3,702
15.8
N
Not detected in 9 samples. Monitored
by LTMP only.
Selenium
86
794.3
5.0
N
Remove limits and monitoring from
permit.
Silver
1.0
17.4
3.025
Y
Action Level parameter — no apparent
toxicity, change monitoring to Quarterly
from 2/ Month.
Zinc
856
950.4
283.4
N
Action Level parameter — no apparent
toxicity. Remove monitoring from
permit.
Fact Sheet
NPDES NC0021873
Renewal
Page 4
RPA — 4.5 MGD
Parameter
Chronic
Allowable
(!L)
Acute
Allowable
(NIIL)
Maximum
Predicted
01L)
RP
�
Comments
Arsenic AL
587.5
N/A
7.9
N
Monitored by LTMP only
Arsenic
HE
529.1
N/A
7.9
N
Monitored by LTMP only.
Cadmium
23.5
146.9
12.3
N
Monitored by LTMP only
Chromium
587.5
10,009.8
886.0
Y
Add Limits and Monthly Monitoring
Copper
82.3
71.5
107
Y
Action Level parameter — no apparent
toxicity, Change monitoring to Quarterly
from 2/ Month.
Cyanide
58.8
215.5
15.8
N
Monitored by LTMP only
Lead
293.8
331.0
6.6
N
Remove limit and monitoring.
Mercury
12 ng/L
N/A
729.6 ng/L
y
Add 47 ng/ L Annual Average limit with
Quarterly monitoring per TMDL.
Nickel
1,034
2556.3
15.8
N
Not detected in 9 samples. Monitored
by LTMP only.
Selenium
59
548.6
5.0
N
Remove limit and monitoring.
Silver
0.7
12
3.025
Y
Action Level parameter — no apparent
toxicity, change monitoring to Quarterly
from 2/ Month.
Zinc
588
656.2
27
N
Action Level parameter — no apparent
toxicity. Remove monitoring from
permit.
RENEWAL SUMMARY
The following changes have been made from the current permit:
• Add TRC footnote per permitting strategy.
• Revise annual effluent parameter scan to 3 scans per permit cycle during specified years in accordance
with revised EPA requirements.
• Adjust ammonia limits to not higher than 35 mg/ L.
• All monitoring requirements of the LTMP remain in place.
• A mercury limit of 47 Ng/ L annual limit with Quarterly monitoring has been added to all flow sheets
in keeping with the Statewide Mercury TMDL; the old weekly average mercury limit of 0. 14 µg/ L on
the 4.5 MGD sheet was removed. See attached Mercury WQBEL/ TBEL Evaluation worksheets for
each flow regime.
• A Mercury Minimization Plan (MMP) has been added as Condition A.(7.) in accordance with the
recent mercury TMDL implementation strategy. See attached NPDES Permitting for Mercury
Implementation of 2012 Statewide Mercury TMDL.
• Based on RPA at 2.5 MGD, Sheet A.(1): removed monitoring for lead, selenium, and zinc, based on
RPA. Removed limits for Total Lead (Daily Max) and Total Selenium (Weekly Average and Daily
Max), based on both acute and chronic standards RPA. Changed to Quarterly monitoring for copper
and silver in accordance with our Permitting Strategy for metals. Add Quarterly monitoring for
chromium. Add annual average limit and quarterly monitoring for mercury based on the recently
approved Mercury TMDL and the Division's implementation strategy. See attached RPA summary
sheets for all 3 RPA runs.
Fact Sheet
NPDES NC0021873
Renewal
Page 5
• Based on RPA at 3.0 MGD, Sheet A.(2): removed monitoring for lead, selenium, and zinc based on
RPA. Removed limits for Total Lead (Daily Max), and Total Selenium (both Weekly Average and Daily
Max), based on standards RPA. Changed to Quarterly monitoring for copper and silver. Add Monthly
average and Daily Maximum limits with monthly monitoring for chromium, and annual average limit with
quarterly monitoring for mercury.
• Based on RPA at 4.5 MGD, Sheet A.(3): removed monitoring for lead, selenium, and zinc, based on
RPA. Removed limits for Total Lead (Daily Max), mercury (Weekly Average) and Total Selenium
(both Weekly Average and Daily Max), based on standards RPA. Changed to Quarterly monitoring for
copper and silver. Add Monthly average and Daily Maximum limits with monthly monitoring for
chromium, and annual average limit with quarterly monitoring for mercury.
• The facility requested reduction in monitoring frequency for BOD, TSS, Ammonia - Nitrogen and Fecal
Coliform based on operating data and the recent Division Strategy for Exceptionally Performing
Facilities. Data submitted were reviewed; BOD, TSS, and Ammonia -Nitrogen meet the criteria, fecal
coliform does not. See attached work sheet DWQ Guidance Regarding the Reduction of
Monitoring Frequencies in NPDES Permits for Exceptionally Performing Facilities (October 22,
2012). As a result, monitoring frequency for BOD, TSS and Ammonia -Nitrogen is reduced to 2 per
week for all three flow regimes, as the current facility is rated and permitted for 4.5 MGD; no
expansion or new construction is required to go up the flow regime limits pages. Fecal coliform
monitoring remains at 3 per week for the 2.5 MGD flow regime, and daily for the 3.0 and 4.5 MGD
regimes.
DRAFT REVIEW COMMENTS
NC Wildlife Resources Commission (WRC) did make comments on the draft renewal permit due to the
presence of rare, threatened and endangered aquatic species, including mussels and fish. Specifically they
requested that we encourage the permittee to consider switching disinfection to UV or Ozone instead of
Chlorine, and that we investigate developing site specific limits for ammonia -nitrogen.
In response, we did agree to add language to the permit issuance cover page discussing the WRC concerns and
to strongly request the permittee to consider UV or other alternate to chlorination, and to keep working on
controlling ammonia -nitrogen discharges. It was pointed out that the recent TRC analysis have all been below
detect, and the facility has passed all WET tests since one failed test in April, 2000. The existing NH3-N data
was reviewed and in -stream concentrations were calculated from DMR data using 7Q10 dilution and the
Division's standard background ammonia-N concentration of 0.22 mg/ L. The results showed mostly
background to slightly above background ammonia-N of 0.22 - 0.25 mg/ L, with one hit at 0.45 mg/ L in
2010. See attached Ammonia-N predicted Instream Concentrations, Mayo WWTP 2010 - October 2012.
PROPOSED SCHEDULE FOR PERMIT ISSUANCE
Draft Permit to Public Notice:
Permit Scheduled to Issue:
Permit Effective Date:
January 2013
July 2013 (Est.)
August 1, 2013
Fact Sheet
NPDES NC0021873
Renewal
Page 6
NPDES DIVISION CONTACT
If you have questions regarding any of the above information or on the attached permit, please contact Jim
McKay at (919) 807-6404 or by email at James.McKay@ncdenr.gov.
NAME:
/
/1 c
REGIONAL OFFICE COMMENTS
DATE: /; / sue'' /2 D / iz
NAME: DATE:
SUPERVISOR: DATE:
NPDES SUPERVISOR: DATE:
Fact Sheet
NPDES NC0021873
Renewal
Page 7
Freshwater RPA
Table 1. Project Information
❑ CHECK if HQW or ORW only
Facility Name
WWTP/WTP Class
NPDES Permit
Outfall
Flow, Qw (MGD)
Receiving Stream
Stream Class
7Q10s (cfs)
7Q10w (cfs)
30Q2 (cfs)
QA (cfs)
1Q10s (cfs)
Data Source(s)
Mayodan WWTP
III
NC0021873
001
2.500
Mayo River
C
75.00
131.00
152.00
362.00
61.34
❑ CHECK for MODEL
DMRs 2010 - 2012 YTD
Follow directions for data entry. In some cases a
comment menu list the available choices or a
dropdown menu will provide a list you may select
from. Error message occur if data entry does not
meet input criteria.
REQUIRED DATA ENTRY
Table 2. Parameters of Concern
Par01
Par02
Par03
Par04
Par05
Par06
Par07
ParOB
Par09
Par10
Par11
Par12
Par13
Par14
Parts
Par16
Par17
Par16
Par19
Par20
Par21
Par22
Name
Tyl:e Chronic
�ecieer Acute
PQL Units
Arsenic
C
50
FW
ug/L
Arsenic
C
10
HHNVS
ug/L
Beryllium
NC
6.5
FW
ug/L
Cadmium
NC
2
FW
15
ug/L
Chlorides (AL)
NC
230
FW
mg/L
Chlorinated Phenolic Compounds
NC
1
A
ug/L
Total Phenolic Compounds
NC
300
A
ug/L
Chromium
NC
50
FW
1,022
ug/L
Copper (AL)
NC
7
FW
7.3
ug/L
Cyanide
NC
5
FW
22
10
ug/L
Fluoride
NC
1,800
FW
ug/L
Lead
NC
25
FW
33.8
ug/L
Mercury
NC
12
FW
0.5
ng/L
Molybdenum
NC
2,000
HH
ug/L
Nickel
NC
88
FW
261
ug/L
Selenium
NC
5
FW
56
ug/L
Silver (AL)
NC
0.06
FW
1.23
ug/L
Zinc (AL)
NC
50
FW
67
ug/L
RPA 21873 2.5 MGD 2012, input
6/14/2013
REASONABLE POTENTIAL ANALYSIS
Arsenic - FW Standard
Date Data BDL=1/2DL Results
1 Jan-10 Std Dev.
2 Feb-10 Mean
3 Mar-10 < 5 2.5 C.V. (default)
4 Apr-10 n
5 May-10
6 Jun-10 Mult Factor =
7 Jul-10 < 5 2.5 Max. Value
8 Aug-10 Max. Pred Cw
9 Sep-10 '< 5 2.5
10 Oct-10
11 Nov-10
12 Dec-10 < 5 2.5
13 Jan-11
14 Feb-11
15 Mar-11 < 5 2.5
16 Apr-11
17 May-11
18 Jun-11 < 5 2.5
19 Jul-11
20 Aug-11
21 Sep-11
22 Oct-11 < 5 2.5
23 Nov-11
24 Dec-11 < 5 2.5
25 Jan-12
26 Feb-12
27 Mar-12 5 2.5
28
SPECIAL-
Values" WITH
"COPY"
0.0000
2.5000
0.6000
9
3.16
2.5 ug/L
7.9 ug/L
Arsenic - HH/WS Standards
Date Data BDL=1/2DL Results
1 Std Dev. 0.0000
2 Mean 2.5000
3 3/1/2010 < 5 2.5 C.V. (default) 0.6000
4 n 9
5
6 Mult Factor = 3.16
7 7/1/2010 < 5 2.5 Max. Value 2.5 ug/L
8 Max. Pred Cw 7.9 ug/L
9 9/1/2010 < 5 2.5
10
11
12 12/1/2010 < 5 2.5
13
14
15 3/1/2011 < 5 2.5
16
17
18 6/1/2011 < 5 2.5
19
20
21
22 10/1/2011 < 5 2.5
23
24 12/1/2011 < 5 2.5
25
26
27 3/1/2012 < 5 2.5
28
THIS SECTION
RPA 21873 2.5 MGD 2012, data
- 1 - 6/14/2013
REASONABLE POTENTIAL ANALYSIS
Cadmium
Date Data BDL=112DL Results
1 Jan-10 < 1 0.5 Std Dev.
2 Feb-10 Mean
3 Mar-10 C.V.
4 Apr-10 n
5 May-10 < 5 2.5
6 Jun-10 Mult Factor =
7 Jul-10 < 1 0.5 Max. Value
8 Aug-10 Max. Pred Cw
9 Sep-10
10 Oct-10 < 1 0.5
11 Nov-10
12 Dec-10
13 Jan-11 <? 1 0.5
14 Feb-11
15 Mar-11
16 Apr-11 s'; 1 0.5
17 May-11
18 Jun-11
19 Jul-11 0.29 0.29
20 Aug-11 < 1 0.5
21 Sep-11
22 Oct-11 < 1 0.5
23 Nov-11
24 Dec-11
25 Jan-12 < 1 0.5
26 Feb-12
27 Mar-12
28
SPECIAL -
Values" WITH
"COPY"
Chromium
0.6432
0.6790
0.9473
10
4.92
2.5 ug/L
12.3 uglL
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
SPECIAL -
Values" WITH
"COPY"
Date Data BDL=1/2DL Results
Jan-10 ci 5 2.5 Std Dev. 18.8156
Feb-10 Mean 8.4500
Mar-10 C.V. 2.2267
Apr 10 n 10
May 10 < 5 2.5
Jun-10 Mult Factor = 14.29
Jul-10 5 2.5 Max. Value 62.0 ug/L
Aug-10 Max. Pred Cw 886.0 ug/L
Sep-10
Oct-10 < 5 2.5
Nov-10
Dec-10
Jan-11 < 5 2.5
Feb-11
Mar-11
Apr-11 < 5 2.5
May-11
Jun-11
Jul-11 62 62
Aug-11 < 5 2.5
Sep-11
Oct-11 5 2.5
Nov-11
Dec-11
Jan-12 < 5 2.5
Feb-12
Mar-12
-2-
RPA 21873 2.5 MGD 2012, data
6/14/2013
REASONABLE POTENTIAL ANALYSIS
Copper (AL)
Date Data BDL=1/2DL Results
1 Jan-10 8.5 8.5 Std Dev.
2 Feb-10 7.5 7.5 Mean
3 Mar-10 6.0 6 C.V.
4 Apr-10 < 10.0 5 n
5 May-10 11.5 11.5
6 Jun-10 9.5 9.5 Mult Factor =
7 Jul-10 8.7 8.7 Max. Value
8 Aug-10 8.5 8.5 Max. Pred Cw
9 Sep-10 18.3 18.3
10 Oct-10 17.0 17
11 Nov-10 12.5 12.5
12 Dec-10 16.0 16
13 Jan-11 17.5 17.5
14 Feb-11 12.0 12
15 Mar-11 6.3 6.3
16 Apr-11 <' 10.0 5
17 May-11 9.5 9.5
18 Jun-11 33.7 33.7
19 Jul-11 41.0 41
20 Aug-11 48.0 48
21 Sep-11 27.0 27
22 Oct-11 31.0 31
23 Nov-11 30.5 30.5
24 Dec-11 27.5 27.5
25 Jan-12 22.5 22.5
26 Feb-12 24.0 24
27 Mar-12 8.7 8.7
28
SPECIAL -
Values" WITH
"COPY"
Cyanide
11.7066
17.5259
0.6680
27
2.23
48.0 ug/L
107.0 ug/L
Date Data BDL=1/2DL Results
1 Jan-10 8 5 Std Dev.
2 Feb-10 Mean
3 Mar 10 C.V. (default)
4 Apr-10
5 May-10 i<: 5 5
6 Jun-10 MuItFactor =
7 Jul-10 < 5 5 Max. Value
8 Aug-10 Max. Pred Cw
9 Sep-10
10 Oct 10 5 5
11 Nov-10
12 Dec-10
13 Jan-11 < 5 5
14 Feb-11
15 Mar-11
16 Apr 11 5 5
17 May-11
18 Jun-11
19 Jul-11
20 Aug-11 <> 5 5
21 Sep-11
22 Oct-11 5 5
23 Nov-11
24 Dec-11
25 Jan-12 < 5 5
26 Feb-12
27 Mar-12
28
SPECIAL -
Values" WITH
"COPY"
0.0000
5.00
0.6000
9
3.16
5.0 ug/L
15.8 ug/L
RPA 21873 2.5 MGD 2012, data
- 3 - 6/14/2013
REASONABLE POTENTIAL ANALYSIS
Lead
Date Data BDL=IJ2DL Results
1 Jan-10 <', 5 2.5 Std Dev.
2 Feb-10 < • 5 2.5 Mean
3 Mar-10 <; 5 2.5 C.V.
4 Apr-10 < 5 2.5 n
5 May-10 < 5 2.5
6 Jun-10 < 5 2.5 Mult Factor =
7 Jul-10 <, 5 2.5 Max. Value
8 Aug-10 5 5 Max. Pred Cw
9 Sep-10 <' 5 2.5
10 Oct-10 < 5 2.5
11 Nov-10 < 5 2.5
12 Dec-10 3.5 3.5
13 Jan-11 <; 5 2.5
14 Feb-11 <• 5 2.5
15 Mar-11 <' 5 2.5
16 Apr-11 < 5 2.5
17 May-11 < 5 2.5
18 Jun-11 <' 5 2.5
19 Jul-11 <' 5 2.5
20 Aug-11 <, 5 2.5
21 Sep-11 < 5 2.5
22 Oct-11 5 2.5
23 Nov-11 4 4
24 Dec-11 < 5 2.5
25 Jan-12 < 5 2.5
26 Feb-12 < 5 2.5
27 Mar-12 < 5 2.5
28
SPECIAL -
Values" WITH
"COPY"
0.5743
2.6652
0.2139
27
Mercury
1.32
5.0 ug/L
6.6 ug/L
Date Data BDL=1/2DL Results
1 3/1/2008 < 200 100 Std Dev. 118.5673
2 8/1/2008 <1 200 100 Mean 68.5056
3 12/1/2008 I 0.00 ERR C.V. 1.7308
4 3/1/2009 0.00 ERR n 16
5 6/1/2009 < 0.20 0.25
6 12/1/2009 0.01 ERR Mult Factor=
7 7/1/2010 0.05 ERR Max. Value
8 12/15/2010 16.00 16 Max. Pred Cw
9 12J22/2010 366.00 366
10 3/1/2011 14.00 14
11 6/1/2011 0.01 ERR
12 10/1/2011 17.00 17
13 12/1/2011 0.08 ERR
14 3/1/2012 0.00 ERR
15 8/2/2012 2.00 2
16 9/27/2012 1.30 1.3
17
18
19
20
21
22
23
24
25
26
27
28
SPECIAL -
Values" WITH
"COPY"
6.98
366.0 ng/L
2554.7 ng/L
-4-
RPA 21873 2.5 MGD 2012, data
6/14/2013
REASONABLE POTENTIAL ANALYSIS
Molybdenum
Date Data BDL=1/2DL Results
1 Jan-10 Std Dev.
2 Feb-10 Mean
3 Mar-10 < 10 5 C.V. (default)
4 Apr-10
5 May-10
6 Jun-10 Mult Factor =
7 Jul-10 < 10 5 Max. Value
8 Aug-10 Max. Pred Cw
9 Sep-10 ;;<, 10 5
10 Oct-10
11 Nov-10
12 Dec-10 < 10 5
13 Jan-11
14 Feb-11
15 Mar-11 < 10 5
16 Apr-11
17 May-11
18 Jun-11 .< 10 5
19 Jul-11
20 Aug-11
21 Sep-11
22 Oct-11 <. 10 5
23 Nov-11
24 Dec-11 5 2.5
25 Jan-12
26 Feb-12
27 Mar-12 10 5
28
SPECIAL -
Values" WITH
"COPY"
0.8333
4.7222
0.6000
9
3.16
5.0 ug/L
15.8 ug/L
Nickel
4
2 Feb-10
3 Mar-10
1 Jan-10 Std Dev.
Apr-10
Date i:at:
10 BDL=1/2DL Results
5 C.V. (default)
Mean
n
5 May-10
6 Jun-10 ", . Mult Factor = 3.16
5.0 uglL
8 Aug-10 Max. Pred Cw 15.8 ug/L
7 Jul-10 .5, 10 5 Max. Value
9 Sep-10 - 10.0 5
10 Oct-10
11 Nov-10
12 Dec-10 <. 10 5
13 Jan-11
14 Feb-11
15 Mar-11 < 10 5
16 Apr-11
17 May-11
18 Jun-11 10 5
19 Jul-11
20
Aug-11
21 Sep-11
22 Oct-11 . < 10 5
23 Nov-11
24 Dec-11 .,< 10 5
25 Jan-12
26 Feb-12
27 Mar-12 <, 10 5
, • ,
28
SPECIAL -
Values" WITH
"COPY"
0.0000
5.0000
0.6000
9
RPA 21873 2.5 MGD 2012, data
-5- 6/14/2013
REASONABLE POTENTIAL ANALYSIS
Selenium
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
Date
Jan-10
Feb-10
Mar-10
Apr-10
May-10
Jun-10
Jul-10
Aug-10
Sep-10
Oct-10
Nov-10
Dec-10
Jan-11
Feb-11
Mar-11
Apr-11
May-11
Jun-11
Jul-11
Aug-11
Sep-11
Oct-11
Nov-11
Dec-11
Jan-12
Feb-12
Mar-12
Apr-12
Data
r'c>
BDL=II2DL Results
10 5 Std Dev.
10 5 Mean
10 5 C.V.
10 5 n
10 5
10 5 Mult Factor =
10 5 Max. Value
10 5 Max. Pred Cw
10 5
10 5
10 5
10 5
10 5
10 5
10 5
10 5
10 5
10 5
10 5
10 5
10 5
10 5
10 5
10 5
10 5
10 5
10 5
10 5
SPECIAL -
Values" WITH
"COPY"
Silver (AL)
0.0000
5.0000
0.0000
28
1.00
5.0 ug/L
5.0 ug/L
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
Date Data BDL=1/2DL Results
Jan-10 < 5 2.5 Std Dev. 0.3257
Feb-10 < 5 2.5 Mean 2.2926
Mar-10 1.8 1.8 C.V. 0.1421
Apr-10 < 5 2.5 n 27
May-10 <' 5 2.5
Jun-10 <'- 5 2.5 Mult Factor =
Jul-10 1.8 1.8 Max. Value
Aug-10 <- 5 2.5 Max. Pred Cw
Sep-10 1.8 1.8
Oct-10 <: 5 2.5
Nov-10 <! 5 2.5
Dec-10 1.8 1.8
Jan-11 c 5 2.5
Feb-11 < 5 2.5
Mar-11 1.8 1.8
Apr-11 <1 5 2.5
May-11 < 5 2.5
Jun-11 1.8 1.8
Jul-11 < 5 2.5
Aug-11 < 5 2.5
Sep-11 <? 5 2.5
Oct-11 1.8 1.8
Nov-11 < 5 2.5
Dec-11 <. 5 2.5
Jan-12 < 5 2.5
Feb-12 <> 5 2.5
Mar-12 1.8 1.8
SPECIAL -
Values" WITH
"COPY"
1.21
2.500 ug/L
3.025 ug/L
-6-
RPA 21873 2.5 MGD 2012, data
6/14/2013
REASONABLE POTENTIAL ANALYSIS
Zinc (AL)
Date Data BDL=112DL Results
1 Jan-10 35.5 35.5 Std Dev. 33.7004
2 Feb-10 44.5 44.5 Mean 72.6407
3 Mar-10 36.7 36.7 C.V. 0.4639
4 Apr-10 25.5 25.5 n 27
5 May-10 22.0 22
6 Jun-10 25.5 25.5 Mult Factor =
7 Jul-10 69.7 69.7 Max. Value
8 Aug-10 54.0 54 Max. Pred Cw
9 Sep-10 78.0 78
10 Oct-10 75.0 75
11 Nov-10 60.5 60.5
12 Dec-10 69.3 69.3
13 Jan-11 95.0 95
14 Feb-11 76.0 76
15 Mar-11 60.3 60.3
16 Apr-11 45.0 45
17 May-11 63.0 63
18 Jun-11 158.3 158.3
19 Jul-11 111.0 111
20 Aug-11 132.0 132
21 Sep-11 112.5 112.5
22 Oct-11 98.0 98
23 Nov-11 103.5 103.5
24 Dec-11 75.5 75.5
25 Jan-12 63.5 63.5
26 Feb-12 108.5 108.5
27 Mar-12 63.0 63
28
SPECIAL.
Values" WITH
"COPY"
1.79
158.3 ug/L
283.4 ug/L
RPA 21873 2.5 MGD 2012, data
- 7 - 6/14/2013
Mayodan WWTP
NC0021873
Qw (MGD) = 2.50
1Q1OS(cfs)= 61.34
7Q1OS (cfs) = 75.00
7Q 10W (cfs) = 131.00
30Q2 (cfs) = 152.00
Avg. Stream Flow, QA (cfs) = 362.00
Receiving Stream: Mayo River
REASONABLE POTENTIAL ANALYSIS
WWTP/WTP Class: Ill
IWC @ 1Q1OS = 5.94%
IWC @ 7Q1OS = 4.91%
IWC @7Q1OW= 2.87%
IWC @ 30Q2 = 2.49%
IWC@QA= 1.06%
Stream Class: C
Outfall 001
Qw=2.5MGD
PARAMETER
TYPE
(1)
STANDARDS & CRITERIA (2)
—i
a
co
i_
z
REASONABLE POTENTIAL RESULTS
RECOMMENDED ACTION
NC WQS / Applied '/ FAV /
Chronic Standard Acute
n# Det. Max Pred Allowable Cw
Cw
Arsenic
Arsenic
C
C
50 FW(7Q10s)
10 HH/WS(Qavg)
ug/L
ug/L
9 0
Note: n < 9
Limited data set
9 0
Note: n <_ 9
7.9
Default C.V.
7.9
Default C.V.
Acute: NO WQS
_ _ _ _ _ _ _ _ _
Chronic: 1,018.3
No o value > Allowable Cw
Chronic 943.4
No value > Allowable Cw
_ _ _ _ _ _ _ _ _ _ _
No- RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
Cadmium
NC
2 FW(7Q10s) 15
ug/L
10 1
12.3
Acute: 252.5
Chronic: 40.7
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
Chromlum
NC
50 FW(7Q10s) 1022
ug/L
10 1
886.0
Acute: 17,205.4
- _____-
Chronic: 1,018.3
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required --- ___
No RP„ Predicted Max a 50% of Allowable Cw -
apply Quarterly Monitoring
Copper (AL)
NC
7 FW(7Q10s) 7
ug/L
27 25
107
Acute: 122.9
Chronic: 142.6
No value > Allowable Cw
No RP , Predicted Max a 50% of Allowable Cw -
apply Quarterly Monitoring
No RP , Predicted Max a 50% of Allowable Cw -
apply Quarterly Monitoring
Cyanide
NC
5 FW(7Q10s) 22
10
ug/L
9 1
Note: n S 9
Limited data set
15.8
Default C.V.
Acute: 370.4
_
Chronic: 101.8
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
Lead
NC
25 FW(7Q10s) 33.8
ug/L
27 3
6.6
Acute: 569.0
- _- _______ --
Chronic: 509.2
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw- No
Monitoring required -- -
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
Mercury
NC
12 FW(7Q10s)
0.5
ng/L
16 13
2,554.7
Acute: NO WQS
Chronic: 244.4
1 value(s) > Allowable Cw
RP, See Mercury: TMDL Evaluation 2.5. MGD
,Monitor Quarterly.
Molybdenum
NC
2000 HH(7Q 10s)
ug/L
9 0
Note: n <_ 9
Limited data set
15.8
Default C.V.
Acute: NO WQS
_ _ _ _ _ _ _ _ _
Chronic: 40,733.2
No value > Allowable Cw
_ _ _ _ _ _ _ _ _ _
No RP, Predicted Max < 50% of Allowable Cw- No
Monitoring required
Nickel
NC
88 FW(7Q10s) 261
ug/L
9 0
Note: n S 9
Limited data set
15.8
Default C.V.
Acute: 4,393.9
Chronic: 1,792.3
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
No RP, Predicted Max < 50% of Allowable Cw- - No
Monitoring required
Page 1 of 2
RPA 21873 2.5 MGD 2012, rpa
6/14/2013
Mayodan WWTP
NC0021873
REASONABLE POTENTIAL ANALYSIS
Outfall 001
Qw=2.5MGD
Selenium
NC
5
FW(7Q10s)
56
ug/L
28
0
5.0
Acute: 942.8
_ _ _ _ _ _ _ _ _
Chronic: 101.8
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable 'Cw- No
Monitoring required _ -
No RP, Predicted Max < 50% of Allowable Cw- No
Monitoring required
Silver (AL)
NC
0.06
FW(7Q 10s)
1.23
ug/L
27
8
3.025
Acute: 20.7
_ _ _ _ _ _ _ _ _ _ _ _ _ _
Chronic: 1.2
27 value(s) > Allowable Cw
No RP, Predicted Max <50% of Allowable Cw = No
Monitoring required _
RP for AL(Cu,Zn,Ag,Fe,CI) - apply Quarterly
Monitoring in conjunction with TOX Test
Zinc (AL)
NC
50
FW(7Q10s)
67
ug/L
27
27
283.4
Acute: 1,127.9
_ _ _ _ _ - _ _ _ -
Chronic: 1,018.3
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required - _ _ _ -
No RP, Predicted Max 50% of Allowable Cw - No
Monitoring required
Page 2 of 2
RPA 21873 2.5 MGD 2012, rpa
6/14/20; 3
Mayodan WWTP
NC0021873
Qw (MGD) = 3.00
1 Q I OS (cfs) = 61.34
7Q 1 OS (cfs) = 75.00
7Q 1 OW (cfs) = 131.00
30Q2 (cfs) = 152.00
Avg. Stream Flow, QA (cfs) = 362.00
Receiving Stream: Mayo River
REASONABLE POTENTIAL ANALYSIS
WWTP/WTP Class: IV
IWC @ 1Q1OS = 7.05%
IWC (a3 7Q10S = 5.84%
IWC cQ 7Q1OW = 3.43%
IWC ® 30Q2 = 2.97%
IWC@QA= 1.27%
Stream Class: C
Outfall 0'01 •
Qw=3MGD
CHRONIC TEST CONCENTRATION = 5.8%
PARAMETER
TYPE
(1)
STANDARDS & CRITERIA (2)
a
I._
Z
REASONABLE POTENTIAL RESULTS
RECOMMENDED ACTION
NC WQS / Applied �/2 FAV /
Chronic Standard Acute
n # Det. Max Pred Allowable Cw
Cw
Arsenic
Arsenic
C
C
50 FW(7QIOs)
10 HI I/WS(Qavg)
ug/L
ug/L
9 0
Note: n < 9
Limited data set
9 0
Note: n < 9
7.9
Default C.V.
7.9
Default C.V.
Acute: NO WQS
_ __ ______ _ __
Chronic: 856.2
No o value > Allowable Cw
Chronic 87.7_4
No value > Allowable Cw
_ _________ ____ _________.
No RP, Predlcted Max < 50% of Allowable Cw - No
Monitoring required
No RP, Predicted Max < 50°% of Allowable Cw - No
Monitoring required
Cadmium
NC
2 FW(7Q10s) 15
ug/L
10 1
12.3
Acute: 212.8
__Ch_r_n_c__-_-3___-
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
NoRP,PredictedMa_x_50_%_o_f Al_lowa_ble_ Cw .N_
Monitoring required
Chromium
NC
50 FW(7Q10s) 1022
ug/L
10 1
886.0
Acute: 14,496.5
Chronic: 856.2
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
RP for non -AL - apply Monthly Monitoring with Limit
Copper (AL)
NC
7 FW(7Q10s) 7
ug/L
27 25
107
Acute: 103.5
_ _ _ _ - _ _ _ _ -
Chronic: 119.9
No value > Allowable Cw
RP for AL(Cu,Zn,Ag,Fe,CI) - apply Quarterly
Monitoring in conjunction with TOX Test _
No RP , Predicted Max a 50% of Allowable Cw -
apply, Quarterly Monitoring
Cyanide
NC
5 FW(7Q10s) 22
10
ug/L
9 1
Note: n < 9
Limited data set
15.8
Default C.V.
Acute: 312.1
_ _ _ _ _ - _ _ _ _ _ _
Chronic: 85.6
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required _ . _ _ _ _ _ _
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
Lead
NC
25 FW(7Q10s) 33.8
ug/L
27 3
6.6
Acute: 479.4
_ _ _ _ _ _ _ _ _ _ _
Chronic: 428.1
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
No RP Predicted' Max < 50% of Allowable Cw - No
Monitoring required
Mercury
NC
12 FW(7Q10s)
0.5
ng/L
16 13
2,554.7
Acute: NO WQS
_ _- -_____ _ __
Chronic: 205.5
l value(s) > Allowable Cw
..
_ _.
RP, See Mercury.TMDLEvaluation 3.0 MGD,
Monitor Quarterly.
Molybdenum
NC
2000 HH(7Q10s)
ug/L
9 0
Note: n _< 9
Limited data set
15.8
Default C.V.
Acute: NO WQS
_ _ _ _ _ _ _ _ _ _ _ _
Chronic: 34,246.6
No value > Allowable Cw
_ _ _ _ _ _ _ _ _ _
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
Nickel
NC
88 FW(7Q10s) 261
ug/L
9 0
Note: n < 9
Limited data set
15.8
Default C.V.
Acute: 3,702.1
_ _ _ _ _ _ _ _ _ -
Chronic: 1,506.8
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required_
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
Page 1 of 2
RPA 21873 3.0 MGD 2012, rpa
6/14/2013
Mayodan WWTP
NC0021873
REASONABLE POTENTIAL ANALYSIS
Outfall 001
Qw=3MGD
Selenium
NC
5
FW(7Q10s)
56
ug/L
28
0
5.0
Acute: 794.3
Chronic: 85.6
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
Silver (AL)
NC
0.06
FW(7Q 10s)
1.23
ug/L
27
8
3.025
Acute: 17.4
Chronic: 1.0
27 value(s) > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
RP for AL(Cu,ZnAg,Fe,CO) - apply Quarterly
Monitoring In conjunction with TOX Test
Zinc (AL)
NC
50
FW(7Q10s)
67
ug/L
27
27
283.4
Acute: 950.4
- _- -_-_-_ _ _-
Chronic: 856.2
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required _-_---------—•
No RP, Predicted Max < 50% of Allowable Cw - No
Monitoring required
Page 2 of 2
RPA 21873 3.0 MGD 2012, rpa
6/14/20r13
Mayodan WWTP
NC0021873
Qw (MGD) = 4.50
1 Q 1 OS (cfs) = 61.34
7Q 10S (cfs) = 75.00
7Q10W (cfs) = 131.00
30Q2 (cfs) = 152.00
Avg. Stream Flow, QA (cfs) = 362.00
Receiving Stream: Mayo River
REASONABLE POTENTIAL ANALYSIS
WWTP/WTP Class: IV
IWC @ 1Q1OS = 10.21%
IWC @7Q10S= 8.51%
IWC ® 7Q1OW = 5.06%
IWC @ 30Q2 = 4.39%
IWC QA 1.89%
Stream Class: C
Outfall 001
Qw=4.5MGD
CHRONIC TEST CONCENTRATION =
PARAMETER
TYPE
(1)
STANDARDS & CRITERIA (2)
g
E
co
t-
zMax
REASONABLE POTENTIAL RESULTS
.
RECOMMENDED ACTION
NC WQS /
Chronic
Applied
Standard
1/2FAV /
Acute
Pred
n # Det. Cw Allowable Cw
Arsenic
Arsenic
C
C
50
10
FW(7Q10s)
HH/WS(Qavg)
ug/L
ug/L
9 0
Note: n < 9
Limited data set
9 0
Note: n < 9
7.9
Default C.V.
7.9
Default C.V.
Acute: NO WQS
_ _________ _ __
Chronic:_____
No value > All_owa_ble Cw_ _
Chronic: 529._1
No value > Allowable Cw
_ _ _ _ _ _ _-_ _
No RP, Predicted Max < 50% of Allowable Cw -
No Monitorin&required _ _ _ _ _ _ _ _ _ C_ _
RP
No , Predicted Max < 50% of Allowable w -
No Monitoring required
Cadmlum
NC
2
FW(7Q10s)
15
ug/L
10 1
12.3
Acute: 146.9
_ _ _ _ _ _ _ _ _ _ _ _
Chronic_ 23.5
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw -
_No_Monitorin&re fired _ _ _ _ _ - _ _ _ - _ _ _
No RP , Predicted Max >_ 50% of Allowable Cw .
apply Quarterly Monitoring
Chromlum
NC
50
FW(7Q10s)
1022
ug/L
10 1
886.0
Acute: 10,009.8
_ __ ____-_ _ _
Chronic: 587.5
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw -
No_Monitorin$reguired _ __-___-_-___
RP for non -AL - apply Monthly Monitoring with
Limit
Copper (AL)
NC
7
FW(7Q10s)
7
ug/L
27 25
107
Acute: 71.5
_ _ _ _ _ _ _ _ _ _ _ _
Chronic: 82.3
No value > Allowable Cw
RP for AL(Cu,Zn,Ag,Fe,CI) - apply Quarterly
Monitorin& n conjunction with TOX Test _ _
RP for AL(Cu,Zn,Ag,Fe,CI) - apply' Quarterly
Monitoring in conjunction with TOX Test
Cyanlde
NC
5
FW(7Q10s)
22
10
ug/L
9 1
Note: n <_ 9
Limited data set
15.8
Default C.V.
Acute: 215.5
_ _ _ _ _ _ _ _ _ _ _ _ _ _
Chronic: 58.8
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw -
_No Monitorin&required _ _ _ .
No RP, Predicted Max < 50% of Allowable Cw -
No Monitoring required
Lead
NC
25
FW(7Q10s)
33.8
ug/L
27 3
6.6
Acute: 331.0
_ _ _ _ _ _ _ _ _ _ _ _ _
Chronic: 293.8
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw -
No Monitoringrequired _ ^ _ , _ _ _ _
No RP, Predicted Max < 50%0 of Allowable Cw -
No Monitoring rewired
Mercury
NC
12
FW(7Q10s)
0.5
ng/L
16 13
2,554.7
Acute: NO WQS
_ _ _ _ _ _ _ _ _
Chronic: 141.0
I value(s) > Allowable Cw
S_ _' _ _ _
—Ricee MercuryTMDL Evaluation 4.5 MGD,
Monitor Quarterly.
Molybdenum
NC
2000
HH(7Q10s)
ug/L
9 0
Note: n < 9
Limited data set
15.8
Default C.V.
Acute: NO WQS
_ _ _ _ _ _ _ _ _ _ _ _
Chronic: 23,501 8
No value > Allowable Cw
_ _ _ _ _ _ _ _ _
No RP, Predicted Max < 50% of Allowable Cw -
No Monitoring required
Nickel
NC
88
FW(7Ql0s)
261
ug/L
9 0
Note: n < 9
Limited data set
15.8
Dcfault C.V.
Acute: 2,556.3
_ ___ _____ _ __
Chronic: 1,034.1
No value > Allowable Cw
No RP, Predicted Max < 50% o of Allowable Cw -
_NoMonitorin&required___________-_
Kai., Predicted Max <50% of Allowable Cw -
No Monitoring required
Page 1 of 2
RPA 21873 4.5 MGD 2012, rpa
6/14/2013
Mayodan WWTP
NC0021873
REASONABLE POTENTIAL ANALYSIS
Outfall 001
Qw = 4.5 MGD
Selenium
NC
5
FW(7Q10s)
56
ug/L
28
0
5.0
Acute: 548.5
_ _ _ _
Chronic: 58.8
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw -
_No_Monitorin uired _ _ _
No RP, Predicted Max < 50% of Allowable Cw -
No Monitoring required
Sllver (AL)
NC
0.06
FW(7Q10s)
1.23
ug/L
27
8
3.025
Acute: 12.0
_ _ _ _ _ — _ — _ _ _ _ — _
Chronic: 0.7
27 value(s) > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw -
No Monitorin�reguired _ _ — _ — _ _ _ _ _ _ — -
RP for AL(Cu,Zn,Ag,Fe,CI) - apply Quarterly
Monitoring in conjunction with TOX Test
Zlnc(AL)
NC
50
FW(7Q10s)
67
ug/L
27
27
283.4
Acute: 656.2
Chronic: 587.5
No value > Allowable Cw
No RP, Predicted Max < 50% of Allowable Cw -
NoMonitorin$reguired _ _ _ _ — _ — -
No RP, Predicted Max < 50% of Allowable Cw -
No Monitoring required
Page 2 of 2
RPA 21873 4.5 MGD 2012, rpa
6/14/20.13
6/14/13 WQS = 12 ng/L MERCURY WQBEL/TBEL EVALUATION V:2012-4
Facility Name: Mayodan WWTP @ 2.5 MGD Annual Limit 47 ng/L with
Quarterly Monitoring
Total Mercury 1631E PQL = 0.5 ng/L 7Q10s = 61.340 cfs WQBEL = 201.96 ng/L
Date Modifier Data Entry Value Permitted Flow = 2.500 MGD TBEL = 47 ng/L
Mar-08
Aug-08
Dec-08
Mar-09
Jun-09
Dec-09
Jul-10
Dec-10
Dec-10
Mar-11
Jun-11
Oct-11
Dec-11
Mar-12
Aug-12
Sep-12
< 200
< 200
0.01
1.80
< 0.20
0.01
0.05
16.00
366.00
14.00
0.01
17.00
0.08
0.00
2.00
1.30
100
100
0.5
1.8
0.5
0.5
0.5
16
366
14
0.5
17
0.5
0
2
1.3
> TBEL
> TBEL
> TBEL
66.8 ng/L - Annual Average for 2008
0.9 ng/L - Annual Average for 2009
127.5 ng/L - Annual Average for 2010
8.0 ng/L - Annual Average for 2011
1.1 ng/L - Annual Average for 2012
6/14/13 WQS = 12 ng/L MERCURY WQBEL/TBEL EVALUATION V:2012-4
Facility Name: Mayodan WWTP @ 3.0 MGD Annual Limit 47 ng/L with
Quarterly Monitoring
Total Mercury 1631E PQL = 0.5 ng/L 7Q10s = 61.340 cfs WQBEL = 170.30 ng/L
Date Modifier Data Entry Value Permitted Flow = 3.000 MGD TBEL = 47 ng/L
Mar-08
Aug-08
Dec-08
Mar-09
Jun-09
Dec-09
Jul-10
Dec-10
Dec-10
Mar-11
Jun-11
Oct-11
Dec-11
Mar-12
Aug-12
Sep-12
< 200 100
< 200 100
0.01 0.5
1.80 1.8
< 0.20 0.5
0.01 0.5
0.05 0.5
16.00 16
366.00 366
14.00 14
0.01 0.5
17.00 17
0.08 0.5
0.00 0
2.00 2
1.30 1.3
> TBEL
> TBEL
> TBEL
66.8 ng/L - Annual Average for 2008
0.9 ng/L - Annual Average for 2009
127.5 ng/L - Annual Average for 2010
8.0 ng/L - Annual Average for 2011
1.1 ng/L - Annual Average for 2012
6/14/13 WQS = 12 ng/L MERCURY WQBEL/TBEL EVALUATION V:2012-4
Facility Name: Mayodan WWTP @ 4.5 MGD Annual Limit 47 ng/L with
Quarterly Monitoring
Total Mercury 1631E PQL = 0.5 ng/L 7Q10s = 61.340 cfs WQBEL = 117.53 ng/L
Date Modifier Data Entry Value Permitted Flow = 4.500 MGD TBEL = 47 ng/L
Mar-08
Aug-08
Dec-08
Mar-09
Jun-09
Dec-09
Jul-10
Dec-10
Dec-10
Mar-11
Jun-11
Oct-11
Dec-11
Mar-12
Aug-12
Sep-12
200 100
200 100
0.01 0.5
1.80 1.8
0.20 0.5
0.01 0.5
0.05 0.5
16.00 16
366.00 366
14.00 14
0.01 0.5
17.00 17
0.08 0.5
0.00 0
2.00 2
1.30 1.3
> TBEL
> TBEL
66.8 ng/L - Annual Average for 2008
0.9 ng/L - Annual Average for 2009
> TBEL WQBEL< 127.5 ng/L - Annual Average for 2010
8.0 ng/L - Annual Average for 2011
1.1 ng/L - Annual Average for 2012
NEapis7, kayo la^ �.•��✓ i P
NPDES Permitting for Mercury
Implementation of 2012 Statewide Mercury TMDL
Facil ty Type '_
Annual Average ` ;i
Linl t Requu ed;(.se ;fit).
on itor tg,Ereciuency
. (ith17 � nalysis)
WO,Required (see B). _
.»
Major Muni (>1 MGD)
CYes)
Quarterly
6Ye if > 2 MGD)
No
3 PPA only
Yes- if multiple detects
above 1 ng/1 and > 2
MGD
Minor Muni (<1 MGD)
Yes
Quarterly
No
No
Once/5 years
No
Industrial
Yes
Quarterly
Yes
No
None in permit. Might
be required for EPA
application form.
No
A.Procedure to Determine if Annual Average Limit Required:
Step 1- WQBEL Evaluation
• Evaluate need for Water Quality Based Effluent Limit (WQBEL)
• Calculate Allowable mercury concentration using dilution (12 ng/1 x 7Q10 dilution factor)
• Compare Annual effluent concentrations to Allowable Conc. for each of last 5 years
• If any Annual Avg > Allowable Conc., then add Annual Avg WQBEL.
Step 2- TBEL Evaluation
• Evaluate need for Technology Based Effluent Limit (TBEL)
• Compare all individual values to TBEL of 47 ng/1
• If any single value > 47 ng/1, then add Annual Avg TBEL of 47 ng/1.
Step 3- Compare WQBEL to TBEL
• If data triggers need for WQBEL and TBEL, select most stringent of the two limits.
• If data triggers need for only TBEL, add 47 ng/1 annual average limit unless WQBEL < 47 ng/1,
in which case annual avg limit should be set at WQBEL.
• Conclusion: the Annual Avg limit will range from 12 ng/1 to upper cap of 47 ng/1.
Step 4- If NEW limit, delay effective date
• Addition of new limit will become effective in 5th year of permit, with mercury minimization plan
development/implementation required for first 4 years (see MMP below).
B. Mercury Minimization Plan (MMP). If an MMP is required (note change to Major Municipal >
2MGD), add the following Special Condition to the permit:
A(x). Mercury Minimization Plan (MMP). The permittee shall develop and implement a mercury
minimization plan during this permit term. The MMP shall be developed within 180 days of the NPDES
Permit Effective Date, and shall be available for inspection on -site. A sample MMP was developed
through a stakeholder review process and has been placed on the Division website for guidance
(http://portal.ncdenr.org/web/wq/swp/ps/npdes, under Model Mercury Minimization Plan). The MMP
should place emphasis on identification of mercury contributors and goals for reduction. Results shall be
summarized and submitted with the next permit renewal.
C. New/Expanding Dischargers- will be allowed as long as the overall aggregate point source load
allocation is not exceeded.
D. Special Situations- Additional site -specific information, such as fish tissue and water column data
when available, will be considered in assigning limits and MMP requirements. Also, limits > TBEL may
be considered on case -by -case basis due to extenuating circumstances
Version 06/13/2013 Prepared by: Tom Belnick Approved by Jeff Poupart
Ne DP 2 1'; 3
-o a•,, D F D la et
DWQ Guidance Regarding the Reduction of Monitoring Frequencies in
NPDES Permits for Exceptionally Performing Facilities
October 22, 2012
A. Purpose
In its efforts to reduce the regulatory burden upon permittees while maintaining adequate compliance
oversight over point source discharges, DWQ has developed the following guidance for the reduction
of monitoring frequencies in NPDES permits for specific target parameters. Standard minimum
NPDES monitoring frequencies are established in 15A NCAC 2B .0508 for discharges from facilities
with specific Standard Industrial Classification (SIC) categories. However, 2B .0508(b)(1) states: "If it
is demonstrated to the satisfaction of the Director that any of the tests and measurements, sampling
points, or frequency of sampling requirements, as required in this Rule for a particular SIC group, are
not applicable to the discharge of a particular water pollution control facility, or if it can be
demonstrated that the objectives of this Section can be achieved by other acceptable means then
such requirements may be waived or modified to the extent that the Director determines to be
appropriate." This document identifies criteria to be used by DWQ that satisfies the regulatory
standard for the allowance of reduced monitoring frequencies for facilities included in SIC 4952.
This guidance applies to facilities with outstanding NPDES program compliance histories, exhibiting
effluent discharges that are excellent in both quality and consistency. Such performance will
demonstrate that compliance for particular parameters can be adequately evaluated with less
monitoring. Facilities demonstrating consistent, long-term treatment performance at levels far below
effluent limitations (<50%) may be considered for a reduction in monitoring from existing permit
frequencies to a 2/week minimum frequency for the parameters BODE, CBOD5 TSS, NH3-N and fecal
coliform/enterococci (the "target parameters").
B. Approval Criteria
Individual NPDES facilities shall submit a written request to modify their NPDES permit specifying
which parameters are to be considered for reduced monitoring . Permit holders must include with
their requests sufficient data, statistical analyses, and other information to support the justification for
reduced monitoring. NPDES permit staff shall review the application and supporting information.
Approval of reduced monitoring frequency shall be granted if all the criteria below are met:
• The facility has no more than one civil penalty assessment for permit limit violations for each
target parameter during the previous three years. /! o & p a-r. 0 / rL 5 ,2/ 2. / / 2 v/ 1
• Neither the permittee nor any of its employees have been convicted of criminal violations of the
Clean Water Act within the previous five years. N on t R A o wm
• The facility is not currently under an SOC for target parameter effluent limit noncompliance. AI't 1.'' to / '
Burs A/el/2v/
• The facility is not on EPA's Quarterly Noncompliance Report for target parameter limit violations. AlVol/ / I,
• For BODS, CBODS, TSS, NH3-N and TSS, the three year arithmetic mean of effluent data must be
less than fifty percent of the onthly average permit limit. For fecal coliform or enterococci, the
i3 oPs T s Aet/5 - r' rt c </
ts , artt -)0 p, fr--- 7Per,PA-- 16 01/4" A d®
50Z is i5 $9 too
3 rr/-l9 tc.o) 9. IA 1,1 Fl 3,, s
Pot, 1 A P f Pir 01 Fa i/
three year geometric mean must be less than 50 percent of the monthly average permit limit. For
parameters with summer and winter limits, an annual arithmetic mean of the seasonal limits may
be used in the calculation.
• With the exception of fecal coliform or enterococci, no more than 15 daily sampling results over
the 3-year review period can be over 200% of the monthly average limit for BOD5, CBOD5, TSS,
or NH3-N . Values associated with documented impacts of extreme weather or e)pnts beyond the
control of the permittee will not be included. r9opf = o 7-55 = / /r✓N1
%a41 /7 /fj
• For fecal coliform or enterococci, no more than 20 daily sampling results may be over 200% of the
weekly average limit. Values associated with documented impacts of extreme weather or events
beyond the control of the permittee will not be included. Te c / y 3
• For the four target parameters, sampling results shall not show more than two non -monthly
average limit violations during the previous year. 1075 = ! NH) - _ °
re5"5 Piss `'a s,5(
• Reduced effluent monitoring must not impair assessment of sensitive downstream uses, such as
endangered species.
C. Implementation
Feed
Fai
After DWQ review and approval, the facility's NPDES permit will be reissued with reduced monitoring
frequencies for qualified parameters. Additional NPDES permit requirements will include:
• Eligible facilities may be granted a reduction from existing permit monitoring frequencies to a
2/week minimum frequency for the four target parameters. Reductions will be made for both
effluent and influent sampling.
• Where monitoring is reduced to twice per week, it must occur on any two non-consecutive days
during the calendar week (Sunday through Saturday).
• Required monitoring frequency reductions establish new permit minimums for monitoring. As
always, facilities may monitor more often than required in the permit.
• If a reportable event, as defined by the permit [e.g., Part 11 (E) (6 & 9)] occurs, any facility granted
reduced monitoring frequencies will be encouraged to monitor on a daily basis until the episode is
resolved.
Monitoring frequency reduction from the minimum frequencies reductions established by the rules are
based upon consistent, exceptional performance. DWQ may revoke on a case -by -case basis these
reductions if the facility begins to perform in noncompliance with permit limits. If a facility's monitoring
reduction for a specific parameter is removed through permit modification, reconsideration of
monitoring frequency reduction will only occur three years following the revocation/permit modification
action, or at the next permit renewal.
• From: Blackwell, Nadine [Nadine.Blackwell@UnitedWater.com]
Sent: Wednesday, February 20, 2013 3:14 PM
To: Mckay, James
Cc: Whitten, Jamie; Michael Brandt (mbrandt@townofmayodan.com)
Subject: RE: Mayodan WWTP Permit Renewal
Attachments: 20130220144610462.pdf; DMR Data for Reduced Monitoring.xls
Thank you for the information.
I am attaching a spread sheet with the Effluent data for BOD, TSS, Ammonia, and Fecal Coliform. As you will
note, the 3 year average is less than 50% of the permit limits for BOD, TSS, and Ammonia. I am also attaching
graphs of the parameters compared to their limits. The weekly TSS was exceeded 2 times during the period and
the weekly Fecal Coliform was exceeded 6 times during the period.
Please let me know if Mayodan qualifies for reduced monitoring for any of the parameters or if you require
additional information. Thanks.
From: Mckay, James [mailto:iames.mckayAncdenr.aov]
Sent: Monday, January 28, 2013 2:42 PM
To: Blackwell, Nadine
Subject: Mayodan WWTP Permit Renewal
Ms. Blackwell:
This link should take you to the document regarding Monitoring Frequency Reduction. You can press "Ctrl"
while clicking on the URL below to go to our NPDES web site, or copy it and paste to your web browser. If you
find that the Mayodan plant meets the requirements, you might be able to cut your monitoring frequency from
3/ week to 2/ week on the specific parameters (BOD, TSS, NH3 — N (Summer) and Fecal Coliform) and save
approximately 1/3 of the lab costs for these parameters. The permit is still in the public comment phase. If you
find that you qualify for a frequency modification, please send me all of the information required, along with any
other comments on the draft permit by 30 days of the date the newspaper ad is published and I will make the
necessary changes to the permit.
http://portal.ncdenr.org/c/document library/get file?uuid=90fdd082-6172-42c0-b4ee-
cf3968502019&groupld=38364
Please contact me if I can be of further assistance.
Jim McKay, Environmental Engineer
NC DENR / Division of Water Quality / Surface Water Protection Section
Point Source Branch
1617 Mail Service Center, Raleigh, NC 27699-1617
919/807-6404 (work); 919/807-6489 (fax)
**Please note, my email address has changed to James.McKay@ncdenr.gov
E-mail correspondence to and from this address may be subject to the North Carolina Public Records law and
may be disclosed to third parties.
file://E:1NC00218731RE Mayodan WWTP Permit Renewal.htm
J A I B I C
D
E
F
G
H
I
J
1
TOWN OF MAYODAN WWTP
2
3
4
BOD
TSS
NH3-N
5
mg/I
mg/I
mg/I
6
1/5/2010
<2.0
1/5/2010
3.50
1/5/2010
0.30
7
1/6/2010
<2.0
1/6/2010
8.30
1/6/2010
0.67
8
1/7/2010
9.00
1/7/2010
6.90
1/7/2010
0.84
9
1/12/2010
<2.0
1/12/2010
6.60
1/12/2010
0.51
10
1/13/2010
<2.0
1/13/2010
9.70
1/13/2010
0.71
11
1/14/2010
2.20
1/14/2010
9.70
1/14/2010
0.83
12
1/19/2010
6.40
1/19/2010
10.00
1/19/2010
2.04
13
1/20/2010
5.50
1/20/2010
16.00
1/20/2010
1.71
14
1/21/2010
3.00
1/21/2010
3.20
1/21/2010
0.23
15
1/26/2010
33.00
1/26/2010
33.00
1/26/2010
3.18
16
1/27/2010
8.20
1/27/2010
24.00
1/27/2010
2.30
17
1/28/2010
5.80
1/28/2010
7.70
1/28/2010
0.69
18
1/29/2010
7.30
1/29/2010
9.00
1/29/2010
0.59
19
2/2/2010
6.30
2/2/2010
17.00
2/2/2010
0.19
20
2/3/2010
3.50
2/3/2010
2.80
2/3/2010
0.17
21
2/4/2010
16.00
2/4/2010
9.30
2/4/2010
3.47
22
2/9/2010
<2.0
2/9/2010
4.00
2/9/2010
0.85
23
2/10/2010
<2.0
2/10/2010
8.30
2/10/2010
0.22
24
2/11/2010
<2.0
2/11/2010
4.70
2/11/2010
0.43
25
2/16/2010
2.60
2/16/2010
1.90
2/16/2010
0.07
26
2/17/2010
5.20
2/17/2010
18.00
2/17/2010
0.12
27
2/18/2010
4.20
2/18/2010
6.60
2/18/2010
0.17
28
2/23/2010
3.40
2/23/2010
14.00
2/23/2010
0.18
29
2/24/2010
2.30
2/24/2010
6.50
2/24/2010
0.14
30
2/25/2010
2.60
2/25/2010
7.10
2/25/2010
0.08
31
3/2/2010
8.20
3/2/2010
6.30
3/2/2010
0.05
32
3/3/2010
4.30
3/3/2010
7.00
3/3/2010
0.05
33
3/4/2010
2.50
3/4/2010
8.30
3/4/2010
0.05
34
3/9/2010
3.80
3/9/2010
2.30
3/9/2010
0.06
35
3/10/2010
<2.0
3/10/2010
2.00
3/10/2010
0.06
36
3/11/2010
<2.0
3/11/2010
10.00
3/11/2010
0.23
37
3/16/2010
5.20
3/16/2010
7.80
3/16/2010
1.02
38
3/17/2010
2.10
3/17/2010
4.50
-
3/17/2010
0.04
39
3/18/2010
2.40
3/18/2010
2.80
3/18/2010
0.09
40
3/23/2010
<2.0
3/23/2010
3.60
3/23/2010
0.38
41
3/24/2010
4.70
3/24/2010
4.00
3/24/2010
0.28
42
3/25/2010
2.10
3/25/2010
6.40
3/25/2010
0.70
43
3/30/2010
11.00
3/30/2010
13.00
3/30/2010
3.48
44
3/31/2010
5.80
3/31/2010
6.70
3/31/2010
1.85
45
4/1/2010
13.00
4/1/2010
4.90
4/1/2010
1.71
46
4/6/2010
2.00
4/6/2010
4.90
4/6/2010
3.31
47
4/7/2010
2.40
4/7/2010
3.80
4/7/2010
3.51
48
4/8/2010
2.90
4/8/2010
4.80
4/8/2010
3.60
49
4/13/2010
5.10
4/13/2010
7.00
4/13/2010
3.58
50
4/14/2010
4.50
4/14/2010
5.40
4/14/2010
3.42
51
4/15/2010
6.90
4/15/2010
8.00
4/15/2010
3.38
52
4/20/2010
2.00
4/20/2010
5.70
4/20/2010
1.67
53
4/21/2010
4.40
4/21/2010
5.30
4/21/2010
1.53
54
4/22/2010
2.40
4/22/2010
8.70
4/22/2010
2.24
55
4/27/2010
17.00
4/27/2010
31.00
4/27/2010
5.44
56
4/28/2010
18.00
4/28/2010
23.00
4/28/2010
12.64
57
4/29/2010
15.00
4/29/2010
15.00
4/29/2010
12.48
58
5/4/2010
13.00
5/4/2010
23.00
5/4/2010
14.68
59
5/5/2010
16.00
5/5/2010
21.00
5/5/2010
19.30
60
5/6/2010
18.00
5/6/2010
25.00
5/6/2010
18.40
I A
B
C
D
E
F
G
H
.I
J
R
61
5/11/2010
17.00
5/11/2010
10.00
5/11/2010
15.76
62
5/12/2010
13.00
5/12/2010
13.00
5/12/2010
12.48
63
5/13/2010
6.10
5/13/2010
6.30
5/13/2010
9.84
64
5/18/2010
33.00
5/18/2010
24.00
5/18/2010
16.12
65
5/19/2010
16.00
5/19/2010
16.00
5/19/2010
12.56
66
5/20/2010
15.00
5/20/2010
8.70
5/20/2010
12.30
67
5/25/2010
13.00
5/25/2010
3.30
5/25/2010
12.92
68
5/26/2010
12.00
5/26/2010
9.10
5/26/2010
14.20
69
5/27/2010
13.00
5/27/2010
8.30
5/27/2010
13.60
70
6/1/2010
19.00
6/1/2010
21.00
6/1/2010
18.72
71
6/2/2010
22.00
6/2/2010
22.00
6/2/2010
21.08
72
6/3/2010
43.00
6/3/2010
16.00
6/3/2010
21.56
73
6/8/2010
26.00
6/8/2010
24.00
6/8/2010
22.60
74
6/9/2010
27.00
6/9/2010
37.00
6/9/2010
22.50
75
6/10/2010
19.00
6/10/2010
22.00
6/10/2010
23.20
76
6/15/2010
16.00
6/15/2010
7.50
6/11/2010
18.90
77
6/16/2010
5.10
6/16/2010
4.60
6/12/2010
20.30
78
6/17/2010
4.60
6/17/2010
2.30
6/13/2010
21.60
79
6/22/2010
4.30
6/22/2010
6.40
6/14/2010
24.10
80
6/23/2010
2.30
6/23/2010
1.30
6/15/2010
12.28
81
6/24/2010
2.80
6/24/2010
1.80
6/16/2010
6.52
82
6/29/2010
4.70
6/29/2010
8.60
6/17/2010
1.95
83
6/30/2010
2.20
6/30/2010
2.20
6/18/2010
1.00
84
7/1/2010
3.40
7/1/2010
5.10
6/19/2010
1.43
85
7/6/2010
2.20
7/6/2010
1.70
6/20/2010
0.65
86
7/7/2010
<2.0
7/7/2010
2.30
6/21/2010
1.44
87
7/8/2010
4.10
7/8/2010
13.00
6/22/2010
6.40
88
7/13/2010
<2.0
7/13/2010
1.00
6/23/2010
0.46
89
7/14/2010
5.90
7/14/2010
6.50
6/24/2010
0.28
90
7/15/2010
4.00
7/15/2010
3.80
6/25/2010
4.08
91
7/20/2010
2.70
7/20/2010
1.00
6/26/2010
4.13
92
7/21/2010
2.20
7/21/2010
2.00
6/27/2010
4.50
93
7/22/2010
2.80
7/22/2010
3.00
6/29/2010
0.84
94
7/27/2010
3.80
7/27/2010
5.00
6/30/2010
1.21
95
7/28/2010
3.00
7/28/2010
5.70
7/1/2010
1.24
96
7/29/2010
2.20
7/29/2010
4.70
7/6/2010
0.16
97
8/3/2010
<2.0
8/3/2010
2.50
7/7/2010
0.22
98
8/4/2010
2.60
8/4/2010
6.80
7/8/2010
0.23
99
8/5/2010
2.80
8/5/2010
3.00
7/13/2010
0.11
100
8/10/2010
<2.0
8/10/2010
4.00
7/14/2010
0.21
101
8/11/2010
2.30
8/11/2010
4.70
7/15/2010
0.39
102
8/12/2010
5.40
8/12/2010
3.00
7/20/2010
0.21
103
8/17/2010
2.40
8/17/2010
3.80
7/21/2010
0.21
104
8/18/2010
<2.0
8/18/2010
2.30
7/22/2010
0.12
105
8/19/2010
2.80
8/19/2010
3.80
7/27/2010
0.39
106
8/24/2010
2.30
8/24/2010
4.40
7/28/2010
0.10
107
8/25/2010
2.10
8/25/2010
5.30
7/29/2010
0.09
108
8/26/2010
2.40
8/26/2010
3.30
8/3/2010
0.30
109
8/31/2010
<2.0
8/31/2010
3.00
8/4/2010
0.10
110
9/1/2010
<2.0
9/1/2010
<4.2
8/5/2010
0.08
111
9/2/2010
<2.0
9/2/2010
7.00
8/10/2010
0.11
112
9/7/2010
<2.0
9/7/2010
<2.8
8/11/2010
0.18
113
9/8/2010
<2.0
9/8/2010
5.30
8/12/2010
0.13
114
9/9/2010
2.90
9/9/2010
8.20
8/17/2010
0.29
115
9/14/2010
<2.0
9/14/2010
3.20
8/18/2010
0.08
116
9/15/2010
<2.0
9/15/2010
2.80
8/19/2010
0.08
117
9/16/2010
<2.0
9/16/2010
4.60
8/24/2010
0.29
118
9/21/2010
<2.0
9/21/2010
<2.6
8/25/2010
1.05
119
9/22/2010
<2.0
9/22/2010
<2.8
8/26/2010
0.18
120
9/23/2010
<2.0
9/23/2010
<2.6
8/31/2010
0.08
A
B
C
D
E
F
G
H
I
I J
121
9/28/2010
<2.0
9/28/2010
2.80
9/1/2010
0.14
122
9/29/2010
2.80
9/29/2010
4.30
9/2/2010
0.10
123
9/30/2010
3.20
9/30/2010
6.40
9/7/2010
0.10
124
•
10/5/2010
<2.0
10/5/2010
3.60
9/8/2010
0.17
125
10/6/2010
<2.0
10/6/2010
<2.8
9/9/2010
1.50
126
10/7/2010
2.20
10/7/2010
4.40
9/14/2010
0.15
127
10/12/2010
<2.0
10/12/2010
3.30
9/15/2010
1.57
128
'
10/13/2010
<2.0
10/13/2010
<2.7
9/16/2010
2.17
129
10/14/2010
2.20
10/14/2010
6.30
9/21/2010
0.18
130
10/19/2010
<2.0
10/19/2010
4.10
9/22/2010
0.14
131
10/20/2010
<2.0
10/20/2010
2.70
9/23/2010
0.20
132
10/21/2010
2.20
10/21/2010
3.20
9/28/2010
0.15
133
10/26/2010
3.70
10/26/2010
<3.8
9/29/2010
2.64
134
10/27/2010
<2.0
10/27/2010
6.00
9/30/2010
0.79
135
10/28/2010
11.00
10/28/2010
52.00
10/5/2010
0.11
136
11 /2/2010
<2.0
11/2/2010
<3.3
10/6/2010
0.09
137
11/3/2010
<2.0
11/3/2010
6.40
10/7/2010
0.09
138
11/4/2010
<2.0
11/4/2010
8.80
10/12/2010
0.08
139
11/9/2010
<2.0
11/9/2010
4.60
10/13/2010
0.09
140
11/10/2010
<2.0
11/10/2010
<4.2
10/14/2010
0.04
141
11/11/2010
<2.0
11/11/2010
5.80
10/19/2010
4.89
142
11/16/2010
4.40
11/16/2010
<3.3
10/20/2010
5.35
143
11/17/2010
• 4.40
11/17/2010
6.40
10/21/2010
2.53
144
11/18/2010
<2.0
11/18/2010
7.10
10/26/2010
0.14
145
11 /22/2010
2.30
11/22/2010
<6.3
10/27/2010
0.12
146
11/23/2010
<2.0
11/23/2010
7.80
10/28/2010
2.20
147
11/24/2010
<2.0
11/24/2010
5.50
11/2/2010
0.38
148
11/30/2010
<2.0
11/30/2010
<4.2
11/3/2010
0.33
149
12/1/2010
<2.0
12/1/2010
<5.0
11/4/2010
0.40
150
12/2/2010
8.10
12/2/2010
10.00
11/9/2010
1.14
151
12/7/2010
4.00
12/7/2010
<3.3
11/10/2010
0.60
152
12/8/2010
3.80
12/8/2010
9.80
11/11/2010
0.29
153
12/9/2010
<2.0
12/9/2010
13.00
11/16/2010
0.09
154
12/14/2010
4.50
12/14/2010
6.80
11/17/2010
1.81
155
12/15/2010
2.90
12/15/2010
13.00
11/18/2010
0.95
156
12/16/2010
2.00
12/16/2010
4.00
11/22/2010
0.11
157
12/21/2010
<2.0
12/21/2010
3.00
11/23/2010
0.08
158
12/22/2010
<2.0
12/22/2010
3.40
11/24/2010
0.08
159
12/23/2010
<2.0
12/23/2010
<2.7
11/30/2010
0.33
160
12/28/2010
2.10
12/28/2010
<6.3
12/1/2010
0.22
161
12/29/2010
<2.0
12/29/2010
3.40
12/2/2010
4.36
162
12/30/2010
<2.0
12/30/2010
3.30
12/7/2010
2.73
163
1/4/2011
<2.0
1/4/2011
<2.7
12/8/2010
2.83
164
"
1/5/2011
2.30
1/5/2011
6.00
12/9/2010
0.14
165
1/6/2011
2.10
1/6/2011
5.60
12/14/2010
3.55
166
1/11/2011
2.70
1/11/2011
4.00
12/15/2010
3.37
167
1/12/2011
2.70
1/12/2011
3.10
12/16/2010
1.31
168
1/13/2011
<2.0
1/13/2011
3.60
12/21/2010
0.07
169
1/18/2011
<2.0
1/18/2011
6.50
12/22/2010
0.05
170
1/19/2011
<2.0
1/19/2011
3.50
12/23/2010
<0.04
171
1/20/2011
<2.0
1/20/2011
2.70
12/28/2010
<0.04
172
1/25/2011
<2.0
1/25/2011
5.30
12/29/2010
<0.04
173
1/26/2011
<2.0
1/26/2011
4.40
12/30/2010
0.10
174
1/27/2011
2.00
1/27/2011
4.30
1/4/2011
0.16
175
2/1/2011
2.60
2/1/2011
3.10
1/5/2011
0.08
176
2/2/2011
2.90
2/2/2011
4.90
1/6/2011
0.11
177
2/3/2011
4.10
2/3/2011
9.40
1/11/2011
0.13
178
2/8/2011
2.30
2/8/2011
<7.1
1/12/2011
0.17
179
2/9/2011
3.10
2/9/2011
5.80
1/13/2011
0.08
180
2/10/2011
<2.0
2/10/2011
4.30
1/18/2011
0.17
I A
B
C
D
E
F
G
H
I
I J
181
2/15/2011
3.10
2/15/2011
9.50
1/19/2011
0.42
182
2/16/2011
<2.0
2/16/2011
<2.8
1/20/2011
6.25
183
2/17/2011
<2.0
2/17/2011
<2.5
1/25/2011
5.50
184
2/22/2011
<2.0
2/22/2011
3.80
1/26/2011
1.32
185
2/23/2011
<2.0
2/23/2011
<2.5
1/27/2011
0.21
186
2/24/2011
<2.0
2/24/2011
<2.5
2/1/2011
0.23
187
3/1/2011
<2.0
3/1/2011
5.20
2/2/2011
0.10
188
3/2/2011
<2.0
3/2/2011
9.60
2/3/2011
0.08
189
3/3/2011
3.00
3/3/2011
5.70
2/8/2011
0.14
190
3/8/2011
<2.0
3/8/2011
5.10
2/9/2011
0.36
191
3/9/2011
<2.0
3/9/2011
6.30
2/10/2011
0.52
192
3/10/2011
16.00
3/10/2011
30.00
2/15/2011
0.43
193
3/11/2011
15.00
3/11/2011
27.00
2/16/2011
0.12
194
3/15/2011
<2.0
3/15/2011
<7.1
2/17/2011
0.27
195
3/16/2011
<2.0
3/16/2011
2.60
2/22/2011
0.17
196
3/17/2011
<2.0
3/17/2011
4.50
2/23/2011
0.15
197
3/22/2011
2.10
3/22/2011
2.70
2/24/2011
0.19
198
3/23/2011
<2.0
3/23/2011
<2.5
3/1/2011
1.49
199
3/24/2011
3.50
3/24/2011
4.00
3/2/2011
1.47
200
3/29/2011
<2.0
3/29/2011
4.80
3/3/2011
0.39
201
3/30/2011
<2.0
3/30/2011
8.50
3/8/2011
2.03
202
3/31/2011
6.10
3/31/2011
11.00
3/9/2011
0.09
203
4/5/2011
6.40
4/5/2011
13.00
3/10/2011
5.94
204
4/6/2011
5.40
4/6/2011
7.20
3/15/2011
0.12
205
4/7/2011
3.30
4/7/2011
<2.5
3/16/2011
0.11
206
4/12/2011
2.50
4/12/2011
<2.7
3/17/2011
0.10
207
4/13/2011
2.40
4/13/2011
<2.8
3/22/2011
0.12
208
r--
4/14/2011
3.10
4/14/2011
7.30
3/23/2011
0.19
209
4/19/2011
4.40
4/19/2011
6.00
3/24/2011
0.16
210
4/20/2011
5.60
4/20/2011
<5.6
3/29/2011
4.06
211
4/21/2011
<2.0
4/21/2011
<2.5
3/30/2011
4.16
212
4/26/2011
<2.0
4/26/2011
<3.1
3/31/2011
0.73
213
4/27/2011
<2.0
4/27/2011
<2.5
4/5/2011
5.18
214
4/28/2011
<2.0
4/28/2011
<2.6
4/6/2011
5.13
215
5/3/2011
<2.0
5/3/2011
<2.5
4/7/2011
0.43
216
5/4/2011
33.00
5/4/2011
240.00
4/12/2011
0.46
217
5/5/2011
15.00
5/5/2011
10.00
4/13/2011
0.50
218
5/10/2011
<2.0
5/10/2011
<2.5
4/14/2011
0.92
219
5/11/2011
<2.0
5/11/2011
5.00
4/19/2011
6.66
220
5/12/2011
<2.0
5/12/2011
5.10
4/20/2011
3.74
221
5/17/2011
<2.0
5/17/2011
<3.6
4/21/2011
0.15
222
5/18/2011
3.10
5/18/2011
7.10
4/26/2011
0.21
223
5/19/2011
20.00
5/19/2011
15.00
4/27/2011
0.17
224
5/24/2011
3.80
5/20/2011
<5.3
4/28/2011
0.21
225
5/25/2011
3.90
5/21/2011
<5.4
5/3/2011
0.17
226
5/26/2011
3.30
5/24/2011
2.70
5/4/2011
1.24
227
5/31/2011
4.80
5/25/2011
9.80
5/5/2011
4.02
228
6/1/2011
3.80
5/26/2011
6.70
5/10/2011
0.11
229
6/2/2011
2.60
5/31/2011
4.80
5/11/2011
0.11
230
6/7/2011
3.40
6/1/2011
4.90
5/12/2011
1.27
231
6/8/2011
<2.0
6/2/2011
4.10
5/17/2011
0.82
232
6/9/2011
2.70
6/7/2011
6.50
5/18/2011
0.88
233
6/14/2011
3.00
6/8/2011
3.20
5/19/2011
5.72
234
6/15/2011
2.90
6/9/2011
5.20
5/24/2011
0.24
235
6/16/2011
2.30
6/14/2011
4.30
5/25/2011
0.34
236
6/21/2011
4.70
6/15/2011
5.20
5/26/2011
2.52
237
6/22/2011
2.80
6/16/2011
6.40
5/31/2011
0.11
238
6/23/2011
<2.0
6/21/2011
8.60
6/1/2011
0.14
239
6/28/2011
4.00
6/22/2011
8.90
6/2/2011
0.14
240
6/29/2011
3.90
6/23/2011
7.70
6/7/2011
0.20
A
B
C
D
EIF
I
G
H
I
J
241
6/30/2011
2.40
6/28/2011
15.00
6/8/2011
0.15
242
7/5/2011
<2.0
6/29/2011
9.30
6/9/2011
0.20
243
7/6/2011
4.30
6/30/2011
11.00
6/14/2011
0.32
244
7/7/2011
<2.0
7/5/2011
4.90
6/15/2011
0.32
245
7/12/2011
3.50
7/6/2011
14.00
6/16/2011
0.21
246
7/13/2011
<2.0
7/7/2011
10.00
6/21/2011
0.20
247
7/14/2011
2.10
7/12/2011
5.20
6/22/2011
1.30
248
7/19/2011
<2.0
7/13/2011
3.90
6/23/2011
0.21
249
7/20/2011
<2.0
7/14/2011
5.80
6/28/2011
0.26
250
7/21/2011
2.60
7/19/2011
5.80
6/29/2011
0.24
251
7/26/2011
<2.0
7/20/2011
5.50
6/30/2011
0.24
252
7/27/2011
<2.0
7/21/2011
6.60
7/5/2011
0.39
253
7/28/2011
<2.0
7/26/2011
<5.6
7/6/2011
0.34
254
8/2/2011
<2.0
7/27/2011
<3.1
7/7/2011
0.16
255
8/3/2011
<2.0
7/28/2011
6.40
7/12/2011
0.22
256
8/4/2011
<2.0
8/2/2011
<4.5
7/13/2011
0.18
257
8/8/2011
10.00
8/3/2011
8.80
7/14/2011
0.21
258
8/9/2011
<2.0
8/4/2011
9.40
7/19/2011
0.14
259
8/10/2011
<2.0
8/8/2011
22.00
7/20/2011
0.19
260
8/11/2011
<2.0
8/9/2011
6.70
7/21/2011
0.16
261
8/16/2011
<2.0
8/10/2011
11.00
7/26/2011
0.21
262
8/17/2011
<2.0
8/11/2011
12.00
7/27/2011
0.15
263
8/18/2011
2.30
8/16/2011
13.00
7/28/2011
0.32
264
8/23/2011
<2.0
8/17/2011
18.00
8/2/2011
0.18
265
8/24/2011
2.40
8/18/2011
19.00
8/3/2011
0.14
266
8/25/2011
2.90
8/23/2011
7.70
8/4/2011
0.21
267
8/30/2011
2.20
8/24/2011
14.00
8/8/2011
7.14
268
8/31/2011
2.20
8/25/2011
26.00
8/9/2011
0.15
269
9/1/2011
<2.0
8/30/2011
22.00
8/10/2011
0.15
270
9/6/2011
5.00
8/31/2011
34.00
8/11 /2011
0.16
271
9/7/2011
5.60
9/1/2011
<8.3
8/16/2011
0.16
272
9/8/2011
10.00
9/6/2011
6.20
8/17/2011
0.16
273
9/13/2011
<2.0
9/7/2011
13.00
8/18/2011
0.16
274
9/14/2011
<2.0
9/8/2011
22.00
8/23/2011
0.23
275
9/15/2011
<2.0
9/13/2011
<5.0
8/24/2011
0.21
276
9/20/2011
<2.0
9/14/2011
17.00
8/25/2011
0.15
277
9/21/2011
<2.0
9/15/2011
<8.3
8/30/2011
1.17
278
9/22/2011
<2.0
9/20/2011
4.50
8/31/2011
1.14
279
9/27/2011
<2.0
9/21/2011
5.40
9/1/2011
1.17
280
9/28/2011
2.30
9/22/2011
19.00
9/6/2011
1.19
281
9/29/2011
<2.0
.
9/27/2011
<2.8
9/7/2011
1.78
282
10/4/2011
<2.0
9/28/2011
4.80
9/8/2011
7.14
283
10/5/2011
<2.0
9/29/2011
<3.1
9/13/2011
0.07
284
10/6/2011
<2.0
10/4/2011
7.70
9/14/2011
0.09
285
10/11/2011
2.20
10/5/2011
16.00
9/15/2011
0.14
286
10/12/2011
<2.0
10/6/2011
18.00
9/20/2011
0.19
287
10/13/2011
7.30
10/11/2011
28.00
9/21/2011
0.17
288
10/18/2011
<2.0
10/12/2011
16.00
9/22/2011
12.88
289
10/19/2011
2.30
10/13/2011
13.00
9/27/2011
0.24
290
•
10/20/2011
<2.0
10/18/2011
<3.3
9/28/2011
0.26
291
10/25/2011
4.20
10/19/2011
6.80
9/29/2011
0.10
292
10/26/2011
2.90
10/20/2011
3.40
10/4/2011
0.13
293
10/27/2011
<2.0
10/25/2011
<8.3
10/5/2011
0.11
294
11/1/2011
2.90
10/26/2011
<6.3
10/6/2011
0.15
295
11/2/2011
5.70
10/27/2011
<6.3
10/11/2011
0.30
296
11/3/2011
<2.0
11/1/2011
<6.3
10/12/2011
0.18
297
11/8/2011
3.20
11/2/2011
12.00
10/13/2011
2.28
298
11/9/2011
6.00
11/3/2011
<7.1
10/18/2011
0.07
299
11/10/2011
3.20
11/8/2011
<7.1
10/19/2011
0.12
300
11/15/2011
4.10
11/9/2011
16.00
10/20/2011
0.10
A
B
I C
D
E
F
G
I H
I
J
301
11/16/2011
2.50
11/10/2011
11.00
10/25/2011
0.09
302
11/17/2011
5.80
11/15/2011
16.00
10/26/2011
0.08
303
11/21/2011
5.00
11/16/2011
15.00
10/27/2011
0.23
304
11/22/2011
<2.0
11/17/2011
23.00
11 /1 /2011
0.07
305
11/23/2011
<2.0
11/21/2011
15.00
11/2/2011
0.12
306
11/29/2011
57.00
11/22/2011
<7.7
11/3/2011
0.08
307
11/30/2011
15.00
11/23/2011
12.00
11/8/2011
0.20
308
12/1/2011
9.20
11/29/2011
232.00
11/9/2011
0.10
309
12/2/2011
<2.0
11/30/2011
45.00
11/10/2011
0.07
310
12/6/2011
<2.0
12/1/2011
19.00
11/15/2011
0.10
311
12/7/2011
<2.0
12/2/2011
11.00
11/16/2011
0.15
312
12/8/2011
3.90
12/6/2011
<8.3
11/17/2011
0.10
313
12/13/2011
2.10
12/7/2011
<7.1
11/21/2011
0.06
314
12/14/2011
3.70
12/8/2011
16.00
11/22/2011
0.06
315
12/15/2011
<2.0
12/13/2011
12.00
11/23/2011
0.08
316
12/20/2011
3.10
12/14/2011
<8.3
11/29/2011
4.68
317
12/21/2011
2.20
12/15/2011
7.70
11/30/2011
26.00
318
12/22/2011
2.40
12/20/2011
5.80
12/1/2011
5.86
319
12/27/2011
<2.0
12/21/2011
<5.0
12/2/2011
1.50
320
12/28/2011
5.10
12/22/2011
7.50
12/6/2011
0.21
321
12/29/2011
3.50
12/27/2011
<7.1
12/7/2011
0.12
322
1/3/2012
<2.0
12/28/2011
8.30
12/8/2011
3.65
323
1/4/2012
3.90
12/29/2011
<6.3
12/13/2011
0.09
324
1/5/2012
4.50
1/3/2012
<2.5
12/14/2011
0.15
325
1/10/2012
3.50
1/4/2012
<3.7
12/15/2011
0.06
326
1/11/2012
<2.0
1/5/2012
20.00
12/20/2011
0.04
327
1/12/2012
3.40
1/10/2012
9.00
12/21/2011
0.04
328
1/17/2012
3.90
1/11/2012
6.00
12/22/2011
0.07
329
1/18/2012
5.10
1/12/2012
<7.1
12/27/2011
0.15
330
1/19/2012
2.30
1/17/2012
6.20
12/28/2011
0.08
331
1/24/2012
2.50
1/18/2012
9.30
12/29/2011
<0.04
332
1/25/2012
3.50
1/19/2012
8.00
1/3/2012
0.09
333
1/26/2012
<2.0
1/24/2012
<5.0
1/4/2012
0.12
334
1/31/2012
3.10
1/25/2012
11.00
1/5/2012
0.10
335
2/1/2012
3.10
1/26/2012
7.50
1/10/2012
0.09
336
2/2/2012
<2.0
1/31/2012
<3.6
1/11/2012
0.07
337
2/7/2012
4.50
2/1/2012
7.10
1/12/2012
0.22
338
2/8/2012
2.50
2/2/2012
<3.3
1/17/2012
0.10
339
2/9/2012
8.90
2/7/2012
8.70
1/18/2012
0.13
340
2/14/2012
4.00
2/8/2012
5.80
1/19/2012
0.06
341
2/15/2012
3.00
2/9/2012
5.50
1/24/2012
0.13
342
2/16/2012
4.10
2/14/2012
10.00
1/25/2012
0.13
343
2/21/2012
13.00
2/15/2012
12.00
1/26/2012
0.12
344
2/22/2012
5.60
2/16/2012
8.70
1/31/2012
0.10
345
2/23/2012
4.80
2/21/2012
20.00
2/1/2012
0.08
346
2/28/2012
2.60
2/22/2012
19.00
2/2/2012
0.11
347
2/29/2012
2.30
2/23/2012
23.00
2/7/2012
0.18
348
3/1/2012
2.80
2/28/2012
<7.7
2/8/2012
0.22
349
3/6/2012
8.70
2/29/2012
<4.2
2/9/2012
0.17
350
3/7/2012
8.60
3/1/2012
<4.2
2/14/2012
0.09
351
3/8/2012
4.30
3/6/2012
<10.0
2/15/2012
0.08
352
3/13/2012
<2.0
3/7/2012
19.00
2/16/2012
0.11
353
3/14/2012
3.60
3/8/2012
9.10
2/21/2012
6.05
354
3/15/2012
4.70
3/13/2012
6.70
2/22/2012
3.46
355
3/20/2012
2.20
3/14/2012
2.90
2/23/2012
0.11
356
3/21/2012
4.10
3/15/2012
5.50
2/28/2012
0.08
357
3/22/2012
<2.0
3/20/2012
3.40
2/29/2012
0.08
358
3/28/2012
4.10
3/21/2012
5.30
3/1/2012
0.06
359
3/29/2012
3.10
3/22/2012
3.60
3/6/2012
2.00
360
3/30/2012
<2.0
3/28/2012
5.20
3/7/2012
0.08
A
B
C
D
E
F
G
H
1 1
J
361
4/3/2012
2.00
3/29/2012
3.70
3/8/2012
0.07
362
4/4/2012
<2.0
3/30/2012
<2.5
3/13/2012
0.12
363
4/5/2012
3.10
4/3/2012
5.00
3/14/2012
0.08
364
4/10/2012
2.60
4/4/2012
4.50
3/15/2012
0.06
365
4/11/2012
3.90
4/5/2012
3.20
3/20/2012
0.32
366
4/12/2012
2.30
4/10/2012
11.00
3/21/2012
0.10
367
4/17/2012
<2.0
4/11/2012
6.20
3/22/2012
0.09
368
4/18/2012
3.10
4/12/2012
7.60
3/28/2012
0.77
369
4/19/2012
4.30
4/17/2012
5.10
3/29/2012
0.08
370
.
4/24/2012
39.00
4/18/2012
2.60
3/30/2012
<0.10
371
4/25/2012
2.90
4/19/2012
<2.5
4/3/2012
0.09
372
.
4/26/2012
<2.0
4/24/2012
12.00
4/4/2012
0.05
373
5/1/2012
<2.0
4/25/2012
7.30
4/5/2012
0.07
374
5/2J2012
<2.0
4/26/2012
2.70
4/10/2012
0.20
375
5/3/2012
<2.0
5/1/2012
<2.5
4/11/2012
0.08
376
5/8/2012
<2.0
5/2/2012
4.60
4/12/2012
0.05
377
5/9/2012
3.30
5/3/2012
5.30
4/17/2012
0.24
378
5/10/2012
3.60
5/8/2012
<2.5
4/18/2012
0.17
379
5/15/2012
2.60
5/9/2012
3.60
4/19/2012
0.09
380
5/16/2012
5.20
5/10/2012
4.80
4/24/2012
12.56
381
5/17/2012
<2.0
5/15/2012
4.90
4/25/2012
2.09
382
5/18/2012
<2.0
5/16/2012
16.00
4/26/2012
0.10
383
5/22/2012
<2.0
5/17/2012
3.20
5/1/2012
0.15
384
5/23/2012
<2.0
5/18/2012
<2.5
5/2/2012
0.16
385
5/24/2012
<2.0
5/22/2012
<2.5
5/3/2012
0.04
386
5/29/2012
<2.0
5/23/2012
<2.5
5/8/2012
0.10
387
5/30/2012
2.00
5/24/2012
4.40
5/9/2012
0.13
388
5/31/2012
<2.0
5/29/2012
<2.5
5/10/2012
2.45
389
6/5/2012
2.10
5/30/2012
2.60
5/15/2012
1.54
390
6/6/2012
<2.0
5/31/2012
3.80
5/16/2012
1.66
391
6/7/2012
<2.0
6/5/2012
<2.8
5/17/2012
0.14
392
6/12/2012
2.80
6/6/2012
3.80
5/18/2012
0.20
393
6/13/2012
2.20
6R/2012
<2.8
5/22/2012
0.17
394
6/14/2012
3.60
6/12/2012
11.00
5/23/2012
0.48
395
6/19/2012
4.20
6/13/2012
<2.5
5/24/2012
0.16
396
6/20/2012
<2.0
6/14/2012
5.00
5/29/2012
0.21
397
6/21/2012
2.70
6/19/2012
3.80
5/30/2012
0.19
398
6/26/2012
2.10
6/20/2012
3.70
5/31/2012
0.21
399
6/27/2012
2.30
6/21/2012
3.10
6/5/2012
0.13
400
6/28/2012
<2.0
6/26/2012
<2.5
6/6/2012
0.14
401
7/2/2012
<2.0
6/27/2012
2.80
6/7/2012
0.11
402
7/3/2012
<2.0
6/28/2012
<2.5
6/12/2012
0.17
403
7/4/2012
<2.0
7/2/2012
<2.5
6/13/2012
0.11
404
7/10/2012
<2.0
7/3/2012
3.20
6/14/2012
2.36
405
7/11/2012
<2.0
7/4/2012
<2.5
6/19/2012
0.21
406
7/12/2012
2.60
7/10/2012
10.00
6/20/2012
0.15
407
7/17/2012
2.70
7/11/2012
<2.8
6/21/2012
0.24
408
7/18/2012
2.90
7/12/2012
6.00
6/26/2012
0.17
409
7/19/2012
<2.0
7/17/2012
<2.8
6/27/2012
0.18
410
7/24/2012
4.30
7/18/2012
<2.8
6/28/2012
0.12
411
7/25/2012
<2.0
7/19/2012
<2.5
7/2/2012
0.21
412
7/26/2012
<2.0
7/24/2012
5.10
7/3/2012
0.13
413
7/31/2012
<2.0
7/25/2012
4.30
7/4/2012
0.12
414
8/1/2012
<2.0
7/26/2012
3.60
7/10/2012
0.12
415
8/2/2012
<2.0
7/31/2012
<2.5
7/11/2012
0.22
416
8/7/2012
<2.0
8/1/2012
3.80
7/12/2012
0.70
417
8/8/2012
<2.0
8/2/2012.
<5.6
7/17/2012
0.15
418
8/9/2012
<2.0
8R/2012
9.00
7/18/2012
0.86
419
8/14/2012
<2.0
.
8/8/2012
6.30
7/19/2012
0.40
420
8/15/2012
<2.0
8/9/2012
6.20
7/24/2012
1.23
I A
B
C
D
E
F
G
H
I 1
I J
421
8/16/2012
<2.0
8/14/2012
<4.2
7/25/2012
0.35
422
8/21/2012
5.00
8/15/2012
5.40
7/26/2012
0.13
423
8/22/2012
3.20
8/16/2012
3.40
7/31/2012
0.08
424
8/23/2012
2.50
8/21/2012
5.80
8/1/2012
0.06
425
8/28/2012
<2.0
8/22/2012
10.00
8/2/2012
0.09
426
8/29/2012
<2.0
8/23/2012
6.60
8/7/2012
0.20
427
8/30/2012
<2.0
8/28/2012
3.60
8/8/2012
0.78
428
9/4/2012
2.10
8/29/2012
3.60
8/9/2012
0.92
429
9/5/2012
<2.0
8/30/2012
2.80
8/14/2012
0.15
430
9/6/2012
<2.0
9/4/2012
<2.5
8/15/2012
0.92
431
9/11/2012
<2.0
9/5/2012
<2.5
8/16/2012
0.18
432
9/12/2012
<2.0
9/6/2012
3.90
8/21/2012
4.06
433
9/13/2012
<2.0
9/11/2012
2.70
8/22/2012
5.60
434
9/18/2012
2.10
9/12/2012
<2.5
8/23/2012
1.12
435
9/19/2012
<2.0
•
9/13/2012
4.20
8/28/2012
0.15
436
9/20/2012
2.40
9/18/2012
3.80
8/29/2012
0.11
437
9/25/2012
<2.0
9/19/2012
<2.5
8/30/2012
0.17
438
9/26/2012
2.50
9/20/2012
11.00
9/4/2012
0.71
439
9/27/2012
<2.0
9/25/2012
<3.6
9/5/2012
0.55
440
10/2/2012
5.30
9/26/2012
3.30
9/6/2012
0.13
441
10/3/2012
5.60
9/27/2012
3.50
9/11/2012
0.13
442
10/4/2012
6.90
10/2/2012
3.30
9/12/2012
0.14
443
10/9/2012
6.80
10/3/2012
7.20
9/13/2012
0.14
444
10/10/2012
2.10
10/4/2012
5.30
9/18/2012
0.18
445
10/11/2012
2.30
10/9/2012
5.90
9/19/2012
0.10
446
10/16/2012
3.70
10/10/2012
2.50
9/20/2012
0.15
447
10/17/2012
3.00
10/11/2012
<2.5
9/25/2012
0.24
448
10/18/2012
<2.0
10/16/2012
2.90
9/26/2012
0.10
449
10/23/2012
<2.0
10/17/2012
<2.5
9/27/2012
0.16
450
10/24/2012
2.90
10/18/2012
<2.5
10/2/2012
3.00
451
10/25/2012
<2.0
10/23/2012
3.20
10/3/2012
2.99
452
10/30/2012
<2.0
10/24/2012
<2.5
10/4/2012
3.04
453
10/31/2012
<2.0
10/25/2012
3.60
10/9/2012
5.01
454
11/1/2012
<2.0
10/30/2012
3.20
10/10/2012
0.36
455
11/6/2012
<2.0
10/31/2012
<2.5
10/11/2012
0.09
456
11/7/2012
2.30
11/1/2012
<2.5
10/16/2012
0.37
457
11/8/2012
<2.0
11/6/2012
<2.5
10/17/2012
0.25
458
11/13/2012
2.30
11/7/2012
<3.1
10/18/2012
0.07
459
11/14/2012
<2.0
11/8/2012
<2.5
10/23/2012
0.07
460
11/15/2012
<2.0
11/13/2012
3.40
10/24/2012
0.09
461
11/19/2012
<2.0
11/14/2012
5.20
10/25/2012
0.05
462
11/20/2012
3.40
11/15/2012
<2.5
10/30/2012
0.07
463
11/21/2012
<2.0
11/19/2012
5.00
10/31/2012
0.05
464
11/27/2012
<2.0
11/20/2012
6.20
11/1/2012
0.24
465
11/28/2012
<2.0
11/21/2012
4.40
11/6/2012
0.80
466
11/29/2012
4.40
11/27/2012
<2.5
11/7/2012
0.11
467
12/4/2012
<2.0
11/28/2012
<2.5
11/8/2012
0.19
468
12/5/2012
<2.0
11/29/2012
5.10
11/13/2012
0.13
469
12/6/2012
2.50
12/4/2012
4.70
11/14/2012
0.13
470
12/11 /2012
<2.0
12/5/2012
3.90
11/15/2012
0.08
471
12/12/2012
<2.0
12/6/2012
4.70
11/19/2012
0.09
472
12/13/2012
<2.0
12/11/2012
3.30
11/20/2012
0.04
473
12/18/2012
2.30
12/12/2012
<2.5
11/21/2012
0.04
474
12/19/2012
2.50
12/13/2012
<2.5
11/27/2012
0.09
475
12/20/2012
3.70
12/18/2012
<3.8
11/28/2012
0.17
476
12/26/2012
24.00
12/19/2012
7.80
11/29/2012
0.07
477
12/27/2012
49.00
12/20/2012
7.00
12/4/2012
0.09
478
12/28/2012
8.40
12/26/2012
15.00
12/5/2012
0.12
479
12/30/2012
3.70
12/27/2012
67.00
12/6/2012
0.11
480
12/28/2012
11.00
12/11/2012
0.12
A
B
C
D
E
F
G
H
I
J
481
12/30/2012
5.30
12/18/2012
0.10
482
12/26/2012
6.38
483
484
485
486
Average
6.02
9.75
1.79
487
488
Permit Limit
30
30
16
489
50% of Limit
15
15
8
K
L
I M
1
2
3
4
Fecal Coliform
5
#/100 Col
6
1/5/2010
2.00
7
1/6/2010
3.00
8
1/7/2010
1.00
9
1/12/2010
2.00
10
1/13/2010
<1.0
11
1/14/2010
2.00
12
1/19/2010
<1.0
13
1/20/2010
9.00
14
1/21/2010
1.00
15
1/26/2010
<1.0
16
1/27/2010
<1.0
17
1/28/2010
440.00
18
1/29/2010
1.00
19
2/2/2010
<1.0
20
2/3/2010
<1.0
21
2/4/2010
<1.0
22
2/9/2010
<1.0
23
2/10/2010
2450.00
24
2/11/2010
<1.0
25
2/16/2010
43.00
26
2/17/2010
1.00
27
2/18/2010
2.00
28
2/23/2010
1.00
29
2/24/2010
<1.0
30
2/25/2010
2.00
31
3/2/2010
5.00
32
3/3/2010
<1.0
33
3/4/2010
1.00
34
3/9/2010
<1.0
35
3/10/2010
<1.0
36
3/11/2010
2.00
37
3/16/2010
1.00
38
3/17/2010
1.00
39
3/18/2010
3.00
40
3/23/2010
<1.0
41
3/24/2010
1.00
42
3/25/2010
2.00
43
3/30/2010
2.00
44
3/31/2010
<1.0
45
4/1/2010
<1.0
46
4/6/2010
1.00
47
4/7/2010
<1.0
48
!
4/8/2010
<1.0
49
4/13/2010
<1.0
50
4/14/2010
<1.0
51
4/15/2010
<1.0
52
4/20/2010
<1.0
53
4/21/2010
<1.0
54
4/22/2010
<1.0
55
4/27/2010
<1.0
56
4/28/2010
0.00
57
4/29/2010
<1.0
58
5/4/2010
<1.0
59
5/5/2010
<1.0
60
5/6/2010
<1.0
K
L
M
61
5/11/2010
7.00
62
5/12/2010
7.00
63
5/13/2010
4.00
64
5/18/2010
1.00
65
5/19/2010
9.00
66
5/20/2010
3.00
67
5/25/2010
7.00
68
5/26/2010
<1.0
69
5/27/2010
1.00
70
6/1/2010
2.00
71
6/2/2010
2.00
72
6/3/2010
<4.0
73
6/8/2010
2.00
74
6/9/2010
<1.0
75
6/10/2010
1.00
76
6/15/2010
<1.0
77
6/16/2010
<1.0
78
6/17/2010
4.00
79
6/22/2010
<1.0
80
6/23/2010
1.00
81
6/24/2010
12.00
82
6/29/2010
<1.0
83
6/30/2010
7.00
84
7/1/2010
14.00
85
7/6/2010
8.00
86
7/7/2010
11.00
87
7/8/2010
10.00
88
7/13/2010
11.00
89
7/14/2010
37.00
90
7/15/2010
24.00
91
7/20/2010
26.00
92
7/21/2010
21.00
93
7/22/2010
12.00
94
7/27/2010
26.00
95
7/28/2010
50.00
96
7/29/2010
26.00
97
8/3/2010
16.00
98
8/4/2010
182.00
99
8/5/2010
23.00
100
8/10/2010
31.00
101
8/11/2010
5.00
102
8/12/2010
12.00
103
8/17/2010
4.00
104
8/18/2010
205.00
105
8/19/2010
2650.00
106
8/24/2010
11.00
^107
8/25/2010
3.00
108
8/26/2010
8.00
109
8/31/2010
5.00
110
9/1/2010
11.00
111
9/2/2010
145.00
112
9/7/2010
9.00
113
9/8/2010
36.00
114
9/9/2010
40.00
115
9/14/2010
12.00
116
9/15/2010
<1.0
117
9/16/2010
8.00
118
9/21/2010
13.00
119
9/22/2010
31.00
120
9/23/2010
41.00
K
L
M
121
9/28/2010
2.00
122
9/29/2010
17.00
123
9/30/2010
6000.00
124
10/5/2010
285.00
125
10/6/2010
26.00
126
10/7/2010
4200.00
127
10/12/2010
4.00
128
10/13/2010
3.00
129
10/14/2010
2.00
130
10/19/2010
<1.0
131
10/20/2010
<1.0
132
10/21/2010
2.00
133
10/26/2010
<1.0
134
10/27/2010
51.00
135
10/28/2010
3.00
136
11/2/2010
<1.0
137
11/3/2010
3.00
138
11/4/2010
17.00
139
11/9/2010
<1.0
140
11/10/2010
7.00
141
11/11/2010
10.00
142
11/16/2010
3.00
143
11/17/2010
<1.0
144
11/18/2010
5.00
145
11/22/2010
5.00
146
11/23/2010
1.00
147
11/24/2010
3.00
148
11/30/2010
<1.0
149
12/1/2010
6.00
150
12/2/2010
<1.0
151
12/7/2010
<1.0
152
12/8/2010
8.00
153
12/9/2010
2.00
154
12/14/2010
<1.0
155
12/15/2010
5.00
156
12/16/2010
<1.0
157
12/21/2010
<1.0
158
12/22/2010
6.00
159
12/23/2010
2.00
160
12/28/2010
<1.0
161
12/29/2010
<1.0
162
12/30/2010
2.00
163
1/4/2011
<1.0
164
1/5/2011
<1.0
165
1/6/2011
1.00
166
1/11/2011
14.00
167
1 /12/2011
2.00
168
1/13/2011
1.00
169
1/18/2011
<1.0
170
1/19/2011
<1.0
171
1/20/2011
1.00
172
1/25/2011
<1.0
173
1/26/2011
3.00
174
1/27/2011
1.00
175
2/1/2011
<1.0
176
2/2/2011
2.00
177
2/3/2011
<1.0
178
2/8/2011
1.00
179
2/9/2011
2.00
180
2/10/2011
1.00
I K
L
M
181
2/15/2011
<1.0
182
2/16/2011
<1.0
183
2/17/2011
<1.0
184
2/22/2011
<1.0
185
2/23/2011
<1.0
186
2/24/2011
1.00
187
3/1/2011
1.00
188
3/2/2011
<1.0
189
3/3/2011
8.00
190
3/8/2011
1.00
191
3/9/2011
2.00
192
3/10/2011
60.00
193
3/11/2011
110.00
194
3/15/2011
11.00
195
3/16/2011
1.00
196
3/17/2011
<1.0
197
3/22/2011
<1.0
198
3/23/2011
<1.0
199
3/24/2011
18.00
200
3/29/2011
3.00
201
3/30/2011
4.00
202
3/31/2011
4.00
203
4/5/2011
<1.0
204
4/6/2011
1.00
205
4/7/2011
2.00
206
4/12/2011
2.00
207
4/13/2011
1.00
208
4/14/2011
1.00
209
4/19/2011
1.00
210
4/20/2011
7.00
211
4/21/2011
7.00
212
4/26/2011
1.00
213
4/27/2011
1.00
214
4/28/2011
5.00
215
5/3/2011
3.00
216
5/4/2011
6000.00
217
5/5/2011
<1.0
218
5/10/2011
<1.0
219
5/11/2011
2.00
220
5/12/2011
5.00
221
5/17/2011
6000.00
222
5/18/2011
6000.00
223
5/19/2011
6.00
224
5/24/2011
14.00
225
5/25/2011
<1.0
226
5/26/2011
33.00
227
5/31/2011
3.00
228
6/1/2011
1.00
229
6/2/2011
17.00
230
6/7/2011
8.00
231
6/8/2011
10.00
232
6/9/2011
13.00
233
6/14/2011
275.00
234
6/15/2011
1400.00
235
6/16/2011
850.00
236
6/21/2011
23.00
237
6/22/2011
38.00
238
6/23/2011
25.00
239
6/28/2011
5100.00
240
6/29/2011
6000.00
! K
L
M
241
6/30/2011
6000.00
242
7/1/2011
15.00
243
7/5/2011
570.00
244
7/6/2011
15.00
245
7/7/2011
<1.0
246
7/12/2011
8.00
247
7/13/2011
6.00
248
7/14/2011
6.00
249
7/19/2011
7.00
250
7/20/2011
23.00
251
7/21/2011
38.00
252
7/26/2011
2.00
253
7/27/2011
2.00
254
7/28/2011
3.00
255
8/2/2011
450.00
256
8/3/2011
10.00
257
8/4/2011
3.00
258
8/8/2011
6000.00
259
8/9/2011
<1.0
260
8/10/2011
<1.0
261
8/11/2011
1.00
262
8/16/2011
1.00
263
8/17/2011
375.00
264
8/18/2011
1.00
265
8/23/2011
4.00
266
8/24/2011
17.00
267
8/25/2011
1.00
268
8/30/2011
4.00
269
8/31/2011
6.00
270
9/1/2011
50.00
271
9/6/2011
6000.00
272
9/7/2011
6000.00
273
9/8/2011
6000.00
274
9/9/2011
18.00
275
9/13/2011
145.00
276
9/14/2011
14.00
277
9/15/2011
8.00
278
9/20/2011
1.00
279
9/21/2011
3.00
280
9/22/2011
1.00
281
9/27/2011
2.00
282
9/28/2011
3.00
283
9/29/2011
2.00
284
10/4/2011
2.00
285
10/5/2011
3.00
286
10/6/2011
4.00
287
10/11/2011
5.00
288
10/12/2011
9.00
289
10/13/2011
21.00
290
10/18/2011
<1.0
291
10/19/2011
2.00
292
10/20/2011
1.00
293
10/25/2011
3.00
294
10/26/2011
4.00
295
10/27/2011
1.00
296
11 /1 /2011
2700.00
297
11 /2/2011
14.00
298
11/3/2011
2.00
299
11/8/2011
795.00
300
11/9/2011
6000.00
I K
L
M
301
11/10/2011
15.00
302
11 /11 /2011
<1.0
303
11/15/2011
3.00
304
11/16/2011
47.00
305
11/17/2011
, 6000.00
306
11 /21 /2011
4100.00
307
11/22/2011
5.00
308
11/23/2011
5.00
309
11/29/2011
6000.00
310
11/30/2011
1.00
311
12/1/2011
4.00
312
12/2/2011
1.00
313
12/6/2011
<1.0
314
12/7/2011
<1.0
315
12/8/2011
1.00
316
12/13/2011
2.00
317
12/14/2011
5.00
318
12/15/2011
2.00
319
12/20/2011
2.00
320
12/21/2011
2.00
321
12/22/2011
<1.0
322
12/27/2011
1.00
323
12/28/2011
7000.00
324
12/29/2011
5.00
325
1/3/2012
<1.0
326
1/4/2012
<1.0
327
1/5/2012
1.00
328
1/10/2012
<1.0
329
1/11/2012
<1.0
330
1/12/2012
6000.00
331
1/17/2012
<1.0
332
1/18/2012
2.00
333
1/19/2012
1.00
334
1/24/2012
<1.0
335
1/25/2012
<1.0
336
1/26/2012
<1.0
337
1/30/2012
<1.0
338
1 /31 /2012
33.00
339
2/1/2012
2.00
340
2/2/2012
1.00
341
2/7/2012
<1.0
342
2/8/2012
4.00
343
2/9/2012
3.00
344
2/14/2012
2.00
345
2/15/2012
1.00
346
2/16/2012
5.00
347
2/21/2012
<1.0
348
2/22/2012
10.00
349
2/23/2012
3.00
350
2/28/2012
<1.0
351
2/29/2012
<1.0
352
3/1/2012
1.00
353
3/6/2012
1.00
354
3/7/2012
8.00
355
3/8/2012
4.00
356
3/13/2012
5.00
357
3/14/2012
7.00
358
3/15/2012
1.00
359
3/20/2012
<1.0
360
3/21/2012
<1.0
j K
L
M
361
3/22/2012
2.00
362
3/28/2012
11.00
363
3/29/2012
4.00
364
3/30/2012
17.00
365
4/3/2012
2.00
366
4/4/2012
8.00
367
4/5/2012
3.00
368
4/10/2012
<1.0
369
4/11/2012
1.00
370
4/12/2012
3.00
371
4/17/2012
1.00
372
4/18/2012
1.00
373
4/19/2012
73.00
374
4/24/2012
<1.0
375
4/25/2012
5.00
376
4/26/2012
2.00
377
5/1/2012
<1.0
378
5/2/2012
21.00
379
5/8/2012
3.00
380
5/9/2012
4.00
381
5/10/2012
2.00
382
5/16/2012
6.00
383
5/17/2012
2.00
384
5/18/2012
1.00
385
5/22/2012
1.00
386
5/23/2012
7.00
387
5/24/2012
6.00
388
5/29/2012
10.00
389
5/30/2012
22.00
390
5/31/2012
21.00
391
6/5/2012
11.00
392
6/6/2012
105.00
393
6/7/2012
24.00
394
6/12/2012
31.00
395
6/13/2012
4.00
396
6/14/2012
14.00
397
6/19/2012
4.00
398
6/20/2012
15.00
399
6/21/2012
24.00
400
6/26/2012
1600.00
401
6/27/2012
1350.00
402
6/28/2012
22.00
403
i 7/2/2012
5.00
404
7/3/2012
2.00
405
7/5/2012
6.00
406
7/10/2012
10.00
407
7/11/2012
6.00
408
7/12/2012
5.00
409
7/17/2012
17.00
410
7/18/2012
5650.00
411
7/19/2012
41.00
412
7/24/2012
9.00
413
7/25/2012
51.00
414
7/26/2012
29.00
415
7/30/2012
2.00
416
7/31/2012
2.00
417
8/1/2012
<1.0
418
8/6/2012
<1.0
419
8/7/2012
<1.0
420
8/8/2012
<1.0
K
L
M
421
8/13/2012
9.00
422
8/14/2012
<1.0
423
8/15/2012
10.00
424
8/20/2012
10.00
425
8/21/2012
600.00
426
8/22/2012
<1.0
427
8/27/2012
<1.0
428
8/28/2012
<1.0
429
8/29/2012
4.00
430
9/4/2012
2.00
431
9/5/2012
14.00
432
9/6/2012
140.00
433
9/10/2012
100.00
434
9/11/2012
21.00
435
9/12/2012
2.00
436
9/17/2012
10.00
437
9/18/2012
3.00
438
9/19/2012
1.00
439
9/24/2012
5.00
440
9/25/2012
4.10
441
9/26/2012
23.50
442
10/1/2012
2.00
443
10/2/2012
2.00
444
10/3/2012
<1.0
445
10/8/2012
2420.00
446
10/9/2012
13.40
447
10/10/2012
16.10
448
10/11/2012
<1.0
449
10/12/2012
<1.0
450
10/15/2012
<1.0
451
10/16/2012
1.00
452
10/17/2012
1.00
453
10/22/2012
4.00
454
10/23/2012
2.00
455
10/24/2012
3.00
456
10/29/2012
<1.0
457
10/30/2012
8.50
458
10/31/2012
3.10
459
11/5/2012
<1.0
460
11/6/2012
<1.0
461
11/7/2012
1.00
462
11/12/2012
<1.0
463
11/13/2012
1.00
464
11/14/2012
<1.0
465
11/19/2012
6.30
466
11/20/2012
8.40
467
11 /21 /2012
20.60
468
11/26/2012
<1.0
469
11/27/2012
2.00
470
11/28/2012
13.10
471
12/3/2012
7.20
472
12/4/2012
4.10
473
12/5/2012
7.50
474
12/10/2012
<1.0
475
12/11/2012
6.30
476
12/12/2012
2.00
477
12/17/2012
7.40
478
12/18/2012
7.50
479
12/19/2012
121.00
480
12/26/2012
2420.00
J K
L
M
481
12/27/2012
2420.00
482
12/28/2012
<1.0
483
484
485
486
487
488
200
489
100
40
30
J
E 20
Monthly BOD
10
0 I
0
r
CO
0
r
L.
2
0
CES
0
r
0 CO
Cn Z
c^
a)
0
Z
Date (1 /1 /2010 to 12/31 /2012 )
/ Effluent BOD mg/L (Mo Avg)
N
1
C\I
M
03
WIMS (NC MAYODAN WWTP)
Effluent BOD Monthly
MoMaxLimit
50
OEMR.
Weekly BOD
40
30
J
>)
E
20
10
WklyMaxLimit
0 “iAt.1\ 'v'N,AktIA A yli/APL
1/3/10 4/11/10 7/18/10 10/24/10 1/30/11 5/8/11 8/14/11 11/20/11 2/26/12 6/3/12 9/9/12 12/16/12 3/24/13
Week Ending Dates (1 /1 /2010 to 12/31 /2012 )
/ Effluent BOD mg/L (Wk Avg)
WIMS (NC MAYODAN WWTP)
Effluent BOD Weekly
O
t—
c
as
Monthly TSS
O 0 r-
N > aCfs
0) Z n 2
Date (111/2010 to 12/31/2012 )
/ Effluent TSS mg/L (Mo Avg)
CO
as
WIMS (NC MAYODAN WWTP)
Effluent BOD Monthly
MoMaxLimit
100
80
60
40
20
Weekly TSS
WklyMaxa_imit
0 !
1/3/10 4/11 /10 7/18/10 10/24/10 1/30/11 5/8/11 8/14/11 11/20/11 2/26/12 6/3/12 9/9/12 12/16/12 3/24/13
Week Ending Dates (111/2010 to 12/31/2012)
/ Effluent TSS mg/L (Wk Avg)
WIMS (NC MAYODAN WWTP)
Effluent TSS Weekly
15
10
0 0 0
✓ r r
Monthly Ammonia
0 0 0
T r r r T e-
CD 0 C
CO Z -3 2 2
CNICNINCNINCNI
T r T r r r r
— 3 v - m >
U) Z - CO Z
Date (1/1 /2010 to 12/31 /2012 )
/ Effluent NH3 N mg/L (Mo Avg)
M
cES
—3
WIMS (NC MAYODAN WWTP)
Effluent Ammonia Monthly
25
20
15
J
E
10-
5—
Weekly Ammonia
1/3/10 4/11/10 7/18/10 10/24/10 1/30/11 5/8/11 8/14/11 11/20/11 2/26/12 6/3/12 9/9/12 12/16/12 3/24/13
Week Ending Dates (1/1/2010 to 12/31/2012 )
/ Effluent NH3 N mg/L (Wk Avg)
WIMS (NC MAYODAN WWTP)
Effluent Ammonia Weekly
250
200
150
E
0
0
100
Monthly Fecal Coliform
50
0 0 0 0 0 0
c-
-3
1
1- r- c- r--
�
- N O
2 u) z
(3
i
to
as
N > as O >
�n Z -3 2 2 z
Date (1 /1 /2010 to 12/31 /2012 )
/ Effluent Fecal #/100 Mo (Mo Avg)
N N N N N N M
-3
c
WIMS (NC MAYODAN WWTP)
Effluent BOD Monthly
MoMaxLimit
8000
6000
E
a
0
4000
2000
Weekly Fecal Coliform
—4
Week Ending Dates (1/112010 to 12/31/2012
/ Effluent Fecal #/100 We (Wk Avg)
4 fit- 'I -Ai IA I
WIMS (NC MAYQDAN WWTP)
Effluent Fecal Coliform Weekly
WklyMaxL
North Carolina Wildlife Resources Commission
Gordon Myers, Executive Director
MEMORANDUM
TO: Jim McKay, Surface Water Protection Section — Point Source Branch
Division of Water Quality
FROM: Shari L. Bryant, Piedmont Region Coordinator wit a La
Habitat Conservation Program
DATE: 6 February 2013
SUBJECT: Draft NPDES Permit for Mayodan Wastewater Treatment Plant, Rockingham County,
NPDES Permit No. NC0021873
Biologists with the North Carolina Wildlife Resources Commission have reviewed the subject
document. Our comments are provided in accordance with provisions of the Clean Water Act of 1977 (as
amended), Fish and Wildlife Coordination Act (48 Stat. 401, as amended; 16 U.S.C. 661-667e), North
Carolina General Statutes (G.S. 113-131 et seq.), and North Carolina Administrative Code 15A NCAC
10I.0102.
The Town of Mayodan has applied for a renewal of their NPDES permit to continue to operate an
existing 4.5 MGD wastewater treatment facility. The facility has effluent limitations and monitoring
requirements for 2.5, 3.0, and 4.5 MGD. The 7Q10 is 75 cfs, and the instream waste concentration ranges
from 4.9% to 8.5%. Chlorine is used for disinfection, and effluent limitations for ammonia (NH3 as N)
vary depending on the discharge amount and season. The monthly average ammonia limits range from
9.0 mg/L to 31.5 mg/L. The weekly average ammonia limits range from 27.0 mg/L to 35.0 mg/L.
The wastewater treatment facility discharges to Mayo River, a tributary to Dan River in the
Roanoke River Basin. There are records for the federal and state endangered James spinymussel
(Pleurobema collina) and Roanoke logperch (Percina rex); the federal species of concern and state
endangered green floater (Lasmigona subviridis); the state threatened bigeye jumprock (Moxostoma
ariommum); the state special concern notched rainbow (Villosa constricta) and riverweed darter
(Etheostoma podostemone); and the state significantly rare Roanoke hogsucker (Hypentelium roanokense)
in Mayo River. Also the Significant Natural Heritage Area — Mayo River Aquatic Habitat — is located in
this section of the Mayo River.
Chlorine is acutely toxic and can form secondary compounds that are detrimental to aquatic life.
Valenti (2006) concluded the impact of long term exposure to low doses of chlorine may impact juvenile
mussels and reduce the chance of them being recruited to the reproducing population. Also, fish and
mussel species are very sensitive to ammonia. Dwyer et al. (2005) found that Cape Fear shiners, a federal
endangered fish species, had an IC25 of 8.8 mg/L for ammonia. An IC25 is the level at which an organism
exhibited a 25 percent reduction in a biological measurement such as reproduction or growth after a 7-day
Mailing Address: Division of Inland Fisheries • 1721 Mail Service Center • Raleigh, NC 27699-1721
Telephone: (919) 707-0220 • Fax: (919) 707-0028
Page 2
6 February 2013
Mayodan WWTP
NPDES Permit No. NC0021873
exposure. Augspurger et al. (2003) found that ammonia concentrations which may be protective of
freshwater mussels range from 0.3 to 1.0 mg/L total ammonia as N at pH 8.
We reviewed EPA's Enforcement and Compliance History Online (ECHO) for this facility and it
showed:
• From July 2009 to June 2012 the total residual chlorine was measured at 0 µg/L.
• From July 2009 to June 2012 the total ammonia nitrogen (as N) ranged from a minimum
of 0 mg/L to a maximum of 24.1 mg/L. The average total ammonia nitrogen (as N)
ranged from 0.15 mg/L to 14.35 mg/L.
We recognize the discharge is relatively small, and is located near the confluence of Dan River.
However, the Mayo River supports several federal and state listed species, and several listed species
including the Roanoke logperch have been documented in Dan River. Therefore, it is imperative the
facility operates effectively to prevent excessive discharge of pollutants, particularly chlorine and
ammonia. Should the permit be renewed, we offer the following recommendations to minimize impacts
to aquatic resources.
1. While it appears the facility is not discharging chlorine, we encourage the applicant to consider
replacing chlorine disinfection systems with ultraviolet light or ozone systems to eliminate the
potential for chlorine to be discharged.
2. Develop site -specific acute (short-term) and chronic (long-term) water quality standards for
ammonia to protect rare and sensitive mussel species, particularly James spinymussel in Mayo
River. The site specific standard should be developed using the process described in Appendix A
of the Technical Support Document for Consideration of Federally -listed Threatened or
Endangered Aquatic Species in Water Quality Management Planning for the Goose Creek
Watershed. Please contact Tom Augspurger with the U.S. Fish and Wildlife Service at (919)
856-4520 for additional information on developing a site -specific standard.
Thank you for the opportunity to comment on this permit renewal. If we can be of further
assistance, please contact our office at (336) 449-7625 or shari.bryant@ncwildlife.org.
Literature cited
Augspurger, T., A. E. Keller, M. C. Black, W. G. Cope, and F. J. Dwyer. 2003. Derivation of water
quality guidance for protection of freshwater mussels (Unionidae) from ammonia exposure.
Environmental Toxicology and Chemistry 22(11):2569-2575.
Dwyer, F.J., D.K. Hardesty, C.E. Henke, C.G. Ingersoll, D.W. Whites, T. Augspurger, T.J. Canfield, D.R.
Mount, and F.L. Mayer. 2005. Assessing Contaminant Sensitivity of Endangered and
Threatened Aquatic Species: Part III. Effluent Toxicity Tests. Archives of Environmental
Contamination and Toxicology 48:174-183.
Valenti, T.W., D.S. Cherry, R.J. Currie, R.J. Neves, J.W. Jones, R. Mair, and C.M. Kane. 2006. Chlorine
toxicity to early life stages of freshwater mussels (Bivalvia: Unionidae). Environmental
Toxicology and Chemistry, 25(9):2512-2518.
ec: Rob Nichols, NCWRC
Tom Augspurger, USFWS
Sarah McRae, USFWS
NC0021873
Ammonia-N predicted Instream Concentrations, Mayo WWTP 2010 - October 2012
Based on DMR Data and 7Q10 Flows
Monthly Calculated
Avg. Monthly Avg. Ammonia-N Ammonia-N Ammonia-N
Monthly Avg. Effluent Effluent In -Stream In -Stream Discharge Limit,
Effluent Flow Flow Ammonia-N 7Q10 Concentration Standard (Monthly Avg.)
Date MGD cfs mg/ L cfs mg/ L mg/ L mg/ L
Jan-10 1.487 2.30 1.12 131 0.24 1.8
Feb-10 1.792 2.78 0.51 131 0.23 1.8
Mar-10 1.368 2.12 0.60 131 0.23 1.8
Apr-10 1.063 1.65 4.50 75 0.31 1.0 16
May-10 0.803 1.24 14.35 75 0.45 1.0 16
Jun-10 0.724 1.12 10.47 75 0.37 1.0 16
Jul-10 0.751 1.16 0.28 75 0.22 1.0 16
Aug-10 0.959 1.49 0.23 75 0.22 1.0 16
Sep-10 0.848 1.31 0.71 75 0.23 1.0 16
Oct-10 1.216 1.88 1.31 75 0.25 1.0 16
Nov-10 0.898 1.39 0.51 131 0.22 1.8
Dec-10 1.04 1.61 1.34 131 0.23 1.8
Jan-11 0.884 1.37 1.22 131 0.23 1.8
Feb-11 0.847 1.31 0.23 131 0.22 1.8
Mar-11 1.393 2.16 1.41 131 0.24 1.8
Apr-11 1.108 1.72 1.98 75 0.26 1.0 16
May-11 1.092 1.69 1.35 75 0.24 1.0 16
Jun-11 0.797 1.24 0.30 75 0.22 1.0 16
Jul-11 0.722 1.12 0.22 75 0.22 1.0 16
Aug-11 0.702 1.09 0.77 75 0.23 1.0 16
Sep-11 0.776 1.20 1.96 75 0.25 1.0 16
Oct-11 0.786 1.22 0.32 75 0.22 1.0 16
Nov-11 0.98 1.52 2.28 131 0.24 1.8
Dec-11 0.91 1.41 0.86 131 0.23 1.8
Jan-12 0.911 1.41 0.11 131 0.22 1.8
Feb-12 0.787 1.22 0.83 131 0.23 1.8
Mar-12 1.181 1.83 0.30 131 0.22 1.8
Apr-12 0.921 1.43 1.32 75 0.24 1.0 16
May-12 0.811 1.26 0.50 75 0.22 1.0 16
Jun-12 0.653 1.01 0.34 75 0.22 1.0 16
Jul-12 0.66 1.02 0.36 75 0.22 1.0 16
Aug-12 0.794 1.23 1.04 75 0.23 1.0 16
Sep-12 0.753 1.17 0.23 75 0.22 1.0 16
Oct-12 0.758 1.17 1.11 75 0.23 1.0 16
0.24
Average
0.45
Maximum
0.22
Minimum
Mckay, James
From: Taylor -Smith, Aana
Sent: Monday, June 17, 2013 7:30 AM
To: Mckay, James
Subject: RE: NCoo21873 - Mayodan WWTP
Attachments:. Mayodan WWTP Inspection Letter.pdf
Hi James,
Sorry about that I took a half day on Friday. I have attached a copy of the inspection report for the CEI conducted
4/17/2013. All necessary repairs/maintenance noted in the letter were completed shortly after the inspection. Let me
know if there's anything else I can do for you! T�
Thanks!
Aana Taylor -Smith
Surface Water Protection Section
Winston-Salem Regional Office
Division of Water Quality
Phone: (336) 771-4950
Fax (336) 771-4630
E-mail correspondence to and from this address may be subject to the North Carolina Public Records Law and may be disclosed to
third parties.
From: Mckay, James
Sent: Friday, June 14, 2013 2:58 PM
To: Taylor -Smith, Aana
Subject: NCoo21873 - Mayodan WWTP
Anna:
I am working on renewal of this permit. Per BIMS, you did the most recent compliance review of the facility in April of
this year. Would you please send me a copy of your inspection report? BIMS only refers to your report which covers the
WWTP and I think, a stormwater permit - I can't find the actual report.
Thank you!
Jim McKay, Environmental Engineer
NC DENR / Division of Water Quality / Surface Water Protection Section
Point Source Branch
1617 Mail Service Center, Raleigh, NC 27699-1617
919/807-6404 (work); 919/807-6489 (fax)
**Please note, my email address has changed to James.McKay@ncdenr.gov
E-mail correspondence to and from this address may be subject to the North Carolina Public Records law and may be
disclosed to third parties.
1
From: Bryant, Shari L.
Sent: Wednesday, February 06, 2013 12:43 PM
To: Mckay, James
Subject: RE: NC0021873 Mayodan WWTP
Attachments: NC0021873 Mayodan WWTP_NCWRC.pdf
Jim,
Thank you for sending me the draft file. Please find attached our comments.
Shari Bryant
N.C. Wildlife Resources Commission
P.O. Box 129
Sedalia, NC 27342-0129
336.449.7625
shari.brvant@ncwildlife.org
Get NC Wildlife Update -- news including season dates, bag limits, legislative updates and more -- delivered to
your Inbox from the N.C. Wildlife Resources Commission.
From: Mckay, James
Sent: Tuesday, January 29, 2013 8:26 AM
To: Bryant, Shari L.
Subject: FW: NC0021873 Mayodan WWTP
Shari,
Please see the attached draft file. It went out to notice on January 16, I do not know when it was published in
the newspaper, but the 30 day public notice clock starts with the publication date.
Please send me any questions or comments.
Thank you,
Jim McKay, Environmental Engineer
NC DENR / Division of Water Quality / Surface Water Protection Section
Point Source Branch
1617 Mail Service Center, Raleigh, NC 27699-1617
919/807-6404 (work); 919/807-6489 (fax)
**Please note, my email address has changed to James.McKay@ncdenr.gov
E-mail correspondence to and from this address may be subject to the North Carolina Public Records law and
may be disclosed to third parties.
From: Bryant, Shari L.
Sent: Monday, January 28, 2013 3:58 PM
To: Mckay, James
Subject: NC0021873 Mayodan WWTP
file://E:1NC00218731RE NC0021873 Mayodan WWTP .htm
Jim,
Could you please forward a copy of the draft permit for the Mayodan WWTP (NC0021873)? An electronic copy is
fine.
Thanks.
Shari Bryant
N.C. Wildlife Resources Commission
P.O. Box 129
Sedalia, NC 27342-0129
336.449.7625
shari.bryant@ncwildlife.org
Get NC Wildlife Update -- news including season dates, bag limits, legislative updates and more -- delivered to
your Inbox from the N.C. Wildlife Resources Commission.
Email correspondence to and from this sender is subject to the N.C. Public Records Law and may be disclosed to third parties.
file://E:1N000218731RE NC0021873 Mayodan WWTP .htm
Mkt ittetbsuillt &rui ui
EDEN DAILY NEws
The Messenger
Advertising Affidavit
NCDENR/DWQ/POINT SOURCE BRANCH
1617 MAIL SERVICE CENTER
RALEIGH, NC 27699-1617
P.O. Box 2157
Reidsville, NC 27323-2157
(336) 349-4331
Account Number
3390343
Date
January 20, 2013
Date
Category
Description
Ad Size
01/20/2013
Legal Notices
Public Notice
1 x 32 L
Public Notice
North Carolina Environmental Management
Commission/NPDES lint
1617 Mali Service Center
Raleigh, NC 27699-1617
Notice of Intent to Issue a NPDES
Wastewater Permit
The North Carolina Environmental Manage-
ment Commission proposes to issue a NPDES
wastewater discharge permit to the person(s)
listed below. Written comments regarding the
proposed permit will be accepted until 30 days
after the publish date of this notice. The Direc-
tor of the NC Division of Water Quality (DWQ)
may hold a public hearing should there be a sig-
nificant degree of public interest Please mail
comments and/or information requests to
DWQ at the above address. Interested persons
may visit the DWQ at 512 N. Salisbury Street,
Raleigh, NC to review information on file. Addi-
tional information on NPDES permits and this
notice may be found on our website• J/por
tal.ncdenr.org//web/wq/swp/ps/npde calend
ar, or by caiDn (919) 807-6390. Mayodan re-
quested renewal In Rockingham Coounttyy. this
fa-
cility discharge is treated wastewater to Mayo
River, Roanoke River Basin.
Publisher of the
Reidsville Rev
This is to certify that the attached Public Notice was published by
the Reidsville Rev in the State of North Carolina, on the
following dates:
01/20/2013
The First insertion being given ... 01/20/2013
Newspaper reference: 0002883360
Sworn to and subscribed before me this
sc)- Liantla&f c9O13
Notary Public / Supervis'. r
State of
My Commission expires
SARAH D. GENTRY
Notary Public
Commonwealth of Virginia
Reg. #3206z3
My Commission Expires 1 ���
THIS IS NOT A BILL. PLEASE PAY FROM INVOICE. THANK YOU
NPDES/Aquifer Protection Permitting Unit Pretreatment Information Request Form
PERMIT WRITER COMPLETES THIS PART:
PERMIT WRITERS - AFTER you get this form
back from PERCS:
Check all that apply
- Notify PERCS if LTMP/STMP data we said should
Date of Request
5-Jun-12
municipal renewal
X
be on DMRs is not really there, so we can get it for
Requestor
Jim McKay
new industries
you (or NOV POTW).
Facility Name
Mayodan, town of
WWTP expansion
- Notify PERCS if you want us to keep a specific
Permit Number
NC0021873
Speculative limits
POC in LTMP/STMP so you will have data for next
renewal.
Region
W-SRO
stream reclass.
permit
- Email PERCS draft permit, fact sheet, RPA.
Basin
Roanoke
stream relocation
- Send PERCS paper copy of permit (w/o NPDES
7Q10 change
boilerplate), cover letter, final fact sheet. Email RPA
other
if changes.
other
check a
plicable PERCS staff:
Other Comments to
PERCS:
X...I need information
on Sills and GillsHIW,
LTN, NEU, YAD, ROA - Monti Hassan (371)
BRD, CPF, FRB, TAR - Sarah Morrison (208)
PERCS
Status of
PRETREATMENT STAFF COMPLETES THIS PART:
Pretreatment Program (check all that apply)
1) facility has no SIU's, does have Division approved Pretreatment Program
that is INACTIVE
2) facility has no SIU's, does not have Division approved Pretreatment
Program
3) facili ' :.-s Sills and DWQ approved Pretreatment Program (list "DEN.'"
if program still under development)
f t) u/
3a) '. rogram with LTMP
3b) odified Program with STMP
4) additional conditions regarding Pretreatment attached or listed below
_
STMP time frame:
Most recent:
Flow, MGD
Permitted
Actual
Time eriod for Actual
Next Cycle:
Industrial
0.2t
0 (1-1
V011
Uncontrollable
nla
POC in
LIMP/
STMP
Parameter of
Concern (POC)
Check List
POC due to
NPDES/ Non-
Disch Permit
Limit
Required
by EPA*
Required
by 603
Sludge**
POC due
to SIU***
POTW POC
(Explain
below)'"'**
STMP
Effluent
Freq
IMP
ent
req
1/
BOD
1/
✓.
4
Q M
V
TSS
✓
V
4
Q M
Q Quarterly
V
NH3
1�
4
QM
M= o
Arsenic
1/
4
Q M
4
Cadmium
4
V
4
Q M
4
Chromium
q
4
Q M
4
Copper
4
✓
4
Q M
Cyanide
4
Q M
all data on DMRs?
4
Lead
/
V
q.
✓
4
Q M
YES
Mercury
V
,/
4
Q M
NO (attach data)
V
Molybdenum
'✓
_
4
Q M
4
Nickel
4
✓
4
Q M
Silver
4
Q M
Selenium
✓
V/
4
Q M
4
Zinc
4
V
4
Q M
data in spreadsheet?
Total Nitrogen
4
Q M
YES (email to writer)
Phosphorus
4
Q M
NO
4
Q M
4
Q M
4
Q M
4
Q M
*Always in the LTMP/STMP ** Only in LTMP/STMP if sludge land app or composte (dif POCs for incinerators)
*** Only in LTMP/STMP while SIU still discharges to POTW **** Only in LTMP/STMP when pollutant is still of concem to POTW
Comments to Permit Writer (ex.. explanation of any POCs: Info you have on IU related investigations into NPDES problems): ,
Rtdj 11 UPI r Ctt . c A ITT
I I%In Ok t►. 4% E LrU ilk a--,- Ohl fit ti_
To is 144-- w.f._ . inn If.
(.11111
Pretreatment request fOrmlls
Revised: July 24, 2007
ROANOKE RIVER BASIN: UPPER DAN RIVER SUBBASIN (HUC 03010103)
S301ON3ddV
NC 2010 Integrated Report
All 13,123 Waters in NC are in Category 5-303(d) List for Mercury due to statewide fish consumption advice for several fish species
AU_Number
Category Parameter
AU_Name
AU_Description LengthArea AU_Units Classification
Reason Ihr Rating
Use Category Collection Year 303(d)ycar
Roanoke River Basin Matrimony Creek -Dan River Watershed 0301010305
0 22-30-(10) Mayo River
From dam at Mayodan Water Supply Intake 2.4 FW Miles C
to Dan River
1 Ecological/biological Integrity Benthos Good -Fair Bioclassification Aquatic Life 1999
Q 22-34-(2) Rock House Creek
From Rockingham Countly SR 2381 to Dan 6.5 FW Miles WS-IV
River
1 EcologicaUbiological Integrity Benthos Good -Fair Bioclassilication Aquatic Life 2001
1 Ecological/biological Integrity FishCom Good Bioclassification Aquatic Life 2004
Roanoke River Basin Lower Smith River Watershed 0301010308
Q 22-40-(1) Smith River
5 Copper
From North Carolina -Virginia State Line to a
point 0.8 mile downstream of Rockingham
County SR 1714 (Aiken Road)
2.8 FW Miles WS-IV
Standard Violation Aquatic Life 2008 2008
4s Ecological/biological Integrity Benthos
Fair Bioclassification Aquatic Life
1999 2008
4t Fecal Coliform (recreation)
Standard Violation Recreation 2008 2008
1 Water Quality Standards Water Supply No Criteria Exceeded
Water Supply 2008
C) 22-40-(2.5) Smith River
5 Copper
From a point 0.8 mile downstream of
Rockingham County SR 1714 (Aiken Road)
to Fieldcrest Mills Water Supply Intake
0.5 FW Miles WS-IV;CA
Standard Violation Aquatic Life 2008 2008
4s Ecological/biological Integrity Benthos
Fair Bioclassification Aquatic Life
1999 2008
4t Fecal Coliform (recreation)
Standard Violation Recreation 2008 2008
1 Water Quality Standards Water Supply No Criteria Exceeded
Water Supply 2008
Roanoke River Basin Cascade Creek -Dan River Watershed 0301010309
• 22-48-4 Birch Fork
From source to Wolf Island Creek 8.4 FW Miles C
1 Ecological/biological integrity Benthos Not Impaired Bioclassification Aquatic Life 2007
Q 22-(39)a DAN RIVER (North
Carolina portion)
4t Fecal Coliform (recreation)
From Mill Branch to NC/VA crossing 13.8 FW Miles C
downstream of Wolf Island Creek
Standard Violation Recreation 2008 2008
5 Turbidity
Standard Violation Aquatic Life 2008 2008
Q 22-40-(3) Smith River
5 Copper
From Fieldcrest Mills Water Supply Intake 1.8 FW Miles C
to Dan River
Standard Violation Aquatic Life 2008 2008
4s Ecological/biological integrity Benthos
Fair Bioclassification Aquatic Life
1999 2008
4t Fecal Coliform (recreation) Standard Violation Recreation 2008 2008
1-A.6
QJlckay, James
To:
Subject:
Thank you!
Mickey, Mike
RE: Draft of NPDES permit NC0021873 - Town of Mayodan WWTP
Jim McKay, Environmental Engineer
NC DENR / Division of Water Quality / Surface Water Protection Section
Point Source Branch
1617 Mail Service Center, Raleigh, NC 27699-1617
919/807-6404 (work); 919/807-6489 (fax)
**Please note, my email address has changed to James.McKay@ncdenr.gov
E-mail correspondence to and from this address may be subject to the North Carolina Public Records law and may be
disclosed to third parties.
From: Mickey, Mike
Sent: Monday, January 14, 2013 10:08 AM
To: Mckay, James
Cc: Taylor -Smith, Aana
Subject: RE: Draft of NPDES permit NC0021873 - Town of Mayodan WWTP
James — The draft permit has been reviewed. No corrections or typos noted. Send it on. Mike.
Mike Mickey
Mike.Mickev@NCDENR.gov
NC Division of Water Quality
585 Waughtown Street
Winston-Salem, NC 27107
Phone: (336) 771-4962
FAX: (336) 771-4630
E-mail correspondence to and from this address may be subject to the North
Carolina Public Records Law and may be disclosed to third parties.
From: Mckay, James
Sent: Friday, January 11, 2013 12:44 PM
To: Basinger, Corey; Meadows, Susan; Reid, Steve
Cc: fkcunninghamOdeq.virginia.gov
Subject: Draft of NPDES permit NC0021873 - Town of Mayodan WWTP
Attached is a copy of the draft renewal permit for the Town of Mayodan WWTP. It should go out to public notice and
comment period next Wednesday.
Please send any questions or comments to me.
Thanks,
1
Jim McKay, Environmental Engineer
NC DENR / Division of Water Quality / Surface Water Protection Section
Point Source Branch
1617 Mail Service Center, Raleigh, NC 27699-1617
919/807-6404 (work); 919/807-6489 (fax)
**Please note, my email address has changed to James.McKay@ncdenr.gov
E-mail correspondence to and from this address may be subject to the North Carolina Public Records law and may be
disclosed to third parties.
2
TOWN OF MAYODAN
210 W. MAIN STREET • MAYODAN, N. C. 27027 • (910) 427-0241
FAX (910) 427-7592
December 23, 2011
NCDENR/DWQ
NPDES Unit
1617 Mail Service Center
Raleigh, NC 27699-1617
RE: NC0021873
Dear Mr. Weaver,
Enclosed is the permit renewal application for the Town of Mayodan WWTP.
If you have any questions, please advise.
Sincerely,
Town of Mayodan
._ (L. C.c,„,LAL,
Debra Cardwell
Town Manager
0 EgEDWR R
ig
DEC 19 2011
DENR-WATER QUALITY
POINT SOURCE BRANCH
FACILITY NAME AND PERMIT NUMBER:
Mayodan WWTP , NC0021873
PERMIT ACTION REQUESTED:
Renewal
RIVER BASIN:
Ronoake
SUPPLEMENTAL APPLICATION INFORMATION
PART F. INDUSTRIAL USER DISCHARGES AND RCRA/CERCLA WASTES
All treatment works receiving discharges
complete part F.
GENERAL INFORMATION:
F.1. Pretreatment program. Does the treatment
® Yes ❑ No
F.2. Number of Significant Industrial Users
industrial users that discharge to the
a. Number of non -categorical Sills.
b. Number of CIUs.
SIGNIFICANT INDUSTRIAL USER
Supply the following information for each
provide the information requested for each
from significant industrial users or which receive RCRA,CERCLA, or other remedial wastes must
works have, or is subject ot, an approved pretreatment program?
(SIUs) and Categorical Industrial Users (Gills). Provide the number
treatment works.
2
of each of the following types of
0
INFORMATION:
SIU. If more than one SIU
SIU.
discharges to the treatment works, copy questions F.3 through F.8 and
F.3. Significant Industrial User Information. Provide the name and address of each SIU discharging to the treatment works. Submit additional pages
as necessary.
Name: Unifi Sans
Mailing Address: PO Box 1437
Reidsville, NC 27323
F.4. Industrial Processes. Describe all the industrial processes that affect or contribute to the SIU's discharge.
Melting and extruding nylon chip into fiber
F.5. Principal Product(s) and Raw Material(s). Describe all of the principal processes and raw materials that affect or contribute to the SIU's
discharge.
Principal product(s): Spun nylon fiber
Raw material(s): Nylon 6, 6 chip, 10-12% mineral oil, heat transfer mediums
F.6. Flow Rate.
a. Process wastewater flow rate. Indicate the average daily volume
day (gpd) and whether the discharge is continuous or intermittent.
0.0234 gpd ( X continuous
volume
following:
subcategory?
of process wastewater discharge into
or intermittent)
the collection system in gallons per
into the collection system
b. Non -process wastewater flow rate. Indicate the average daily
in gallons per day (gpd) and whether the discharge is continuous
gpd ( continuous
of non -process wastewater flow discharged
or intermittent.
or intermittent)
F.7. Pretreatment Standards. Indicate whether the SIU is subject to the
a. Local limits ® Yes
b. Categorical pretreatment standards ❑ Yes
If subject to categorical pretreatment standards, which category and
0 No
® No
NPDES FORM 2A Additional Information
FACILITY NAME AND PERMIT NUMBER:
Mayodan WWTP , NC0021873
PERMIT ACTION REQUESTED:
Renewal
RIVER BASIN:
Ronoake
F.8. Problems at the Treatment Works Attributed to Waste Discharge by the SIU. Has the SIU caused or contributed to any problems (e.g.,
upsets, interference) at the treatment works in the past three years?
❑ Yes ® No If yes, describe each episode.
RCRA HAZARDOUS WASTE RECEIVED BY TRUCK, RAIL, OR DEDICATED PIPELINE:
F.9. RCRA Waste. Does the treatment works receive or has it in the past three years received RCRA hazardous waste by truck, rail or dedicated pipe?
❑ Yes El No (go to F.12)
F.10. Waste transport. Method by which RCRA waste is received (check all that apply):
0 Truck ❑ Rail ❑ Dedicated Pipe
F.11. Waste Description. Give EPA hazardous waste number and amount (volume or mass, specify units).
EPA Hazardous Waste Number Amount Units
CERCLA (SUPERFUND) WASTEWATER, RCRA REMEDIATIONICORRECTIVE ACTION
WASTEWATER, AND OTHER REMEDIAL ACTIVITY WASTEWATER:
F.12. Remediation Waste. Does the treatment works currently (or has it been notified that it will) receive waste from remedial activities?
❑ Yes (complete F.13 through F.15.) ® No
F.13. Waste Origin. Describe the site and type of facility at which the CERCLA/RCRA/or other remedial waste originates (or is excepted to origniate in
the next five years).
F.14. Pollutants. List the hazardous constituents that are received (or are expected to be received). Include data on volume and concentration, if
known. (Attach additional sheets if necessary.)
F.15. Waste Treatment.
a. Is this waste treated (or will be treated) prior to entering the treatment works?
❑ Yes ® No
If yes, describe the treatment (provide information about the removal efficiency):
b. Is the discharge (or will the discharge be) continuous or intermittent?
❑ Continuous 0 Intermittent If intermittent, describe discharge schedule.
END OF PART F.
REFER TO THE APPLICATION OVERVIEW (PAGE 1) TO DETERMINE WHICH OTHER PARTS
OF FORM 2A YOU MUST COMPLETE
NPDES FORM 2A Additional Information
FACILITY NAME AND PERMIT NUMBER:
Mayodan WWTP , NC0021873
PERMIT ACTION REQUESTED:
Renewal
RIVER BASIN:
Ronoake
SUPPLEMENTAL APPLICATION INFORMATION
PART F.INDUSTRIAL USER DISCHARGES AND RCRA/CERCLA WASTES
All treatment works receiving discharges from significant industrial users or which receive RCRA,CERCLA, or other remedial wastes must
complete part F.
GENERAL INFORMATION:
F.1. Pretreatment program. Does the treatment works have, or is subject ot, an approved pretreatment program?
® Yes ❑ No
F.2. Number of Significant Industrial Users (SIUs) and Categorical Industrial Users (ClUs). Provide the number of each of the following types of
industrial users that discharge to the treatment works.
c. Number of non -categorical SIUs. 4
d. Number of CIUs. 0
SIGNIFICANT INDUSTRIAL USER INFORMATION:
Supply the following information for each SIU. If more than one SIU discharges to the treatment works, copy questions F.3 through F.8 and
provide the information requested for each SIU.
F.3. Significant Industrial User Information. Provide the name and address of each SIU discharging to the treatment works. Submit additional pages
as necessary.
Name: Unifi 105
Mailing Address: PO Box 1437
Reidsville, NC 27323
F.4. Industrial Processes. Describe all the industrial processes that affect or contribute to the SIU's discharge.
Texturing and covering nyoln fiber
F.5. Principal Product(s) and Raw Material(s). Describe all of the principal processes and raw materials that affect or contribute to the SIU's
discharge.
Principal product(s): Textured and covered nylon fiber
Raw material(s): Nylon fiber, coning oil, light mineral oil
F.6. Flow Rate.
c. Process wastewater flow rate. Indicate the average daily volume of process wastewater discharge into the collection system in gallons per
day (gpd) and whether the discharge is continuous or intermittent.
0.1030 gpd ( X continuous or intermittent)
d. Non -process wastewater flow rate. Indicate the average daily volume of non -process wastewater flow discharged into the collection system
in gallons per day (gpd) and whether the discharge is continuous or intermittent.
gpd ( continuous or intermittent)
F.7. Pretreatment Standards. Indicate whether the SIU is subject to the following:
a. Local limits El Yes ❑ No
b. Categorical pretreatment standards ❑ Yes El No
If subject to categorical pretreatment standards, which category and subcategory?
NPDES FORM 2A Additional Information
¶ACILITY NAME AND PERMIT NUMBER:
Mayodan WWTP , NC0021873
PERMIT ACTION REQUESTED:
Renewal
RIVER BASIN:
Ronoake
F.8. Problems at the Treatment Works Attributed to Waste Discharge by the SIU. Has the SIU caused or contributed to any problems (e.g.,
upsets, interference) at the treatment works in the past three years?
❑ Yes ® No If yes, describe each episode.
RCRA HAZARDOUS WASTE RECEIVED BY TRUCK, RAIL, OR DEDICATED PIPELINE:
F.9. RCRA Waste. Does the treatment works receive or has it in the past three years received RCRA hazardous waste by truck, rail or dedicated pipe?
❑ Yes ® No (go to F.12)
F.10. Waste transport. Method by which RCRA waste is received (check all that apply):
0 Truck 0 Rail 0 Dedicated Pipe
F.11. Waste Description. Give EPA hazardous waste number and amount (volume or mass, specify units).
EPA Hazardous Waste Number Amount Units
CERCLA (SUPERFUND) WASTEWATER, RCRA REMEDIATION/CORRECTIVE ACTION
WASTEWATER, AND OTHER REMEDIAL ACTIVITY WASTEWATER:
F.12. Remediation Waste. Does the treatment works currently (or has it been notified that it will) receive waste from remedial activities?
❑ Yes (complete F.13 through F.15.) ® No
F.13. Waste Origin. Describe the site and type of facility at which the CERCLA/RCRA/or other remedial waste originates (or is excepted to origniate in
the next five years).
F.14. Pollutants. List the hazardous constituents that are received (or are expected to be received). Include data on volume and concentration, if
known. (Attach additional sheets if necessary.)
F.15. Waste Treatment.
c. Is this waste treated (or will be treated) prior to entering the treatment works?
❑ Yes EI No
If yes, describe the treatment (provide information about the removal efficiency):
d. Is the discharge (or will the discharge be) continuous or intermittent?
❑ Continuous ❑ Intermittent If intermittent, describe discharge schedule.
END OF PART F.
REFER TO THE APPLICATION OVERVIEW (PAGE 1) TO DETERMINE WHICH OTHER PARTS
OF FORM 2A YOU MUST COMPLETE
NPDES FORM 2A Additional Information
Bureau of Labor Statistics Data Page 1 of 1
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Change Output
Options:
From: 2001 To: 2011 ,
❑ include graphs
Data extracted on: December 12, 2011 (3:14:21 PM)
Producer Price Index -Commodities
Series Id: WPU06130217
Not Seasonally Adjusted
Group: Chemicals and allied products
Item: Potassium & sodium compounds, ex. bleaches
Base Date: 200106
Down oad: J
More Formatting Optionsy
Year
Jan
Feb
Mar
Apr
May
Jun
Jul
Aug
Sep
Oct
Nov
Dec
Annual
2001
100.0
101.1
99.2
99.3
99.1
99.1
97.7
2002
99.8
97.9
99.7
99.0
98.3
98.9
97.0
97.8
97.9
97.8
98.1
97.5
98.3
2003
97.5
98.3
96.5
97.9
98.8
99.8
98.4
96.4
97.6
98.2
96.8
96.6
97.7
2004
95.9
97.7
99.6
99.6
99.3
100.0
99.7
99.7
101.1
100.9
102.7
104.3
100.1
2005
104.3
105.6
105.1
108.9
110.6
109.8
112.0
113.4
114.3
117.0
122.7
119.9
112.0
2006
121.6
129.6
130.2
135.9
135.6
135.2
139.0
133.6
137.2
135.1
135.6
139.4
134.0
2007
135.6
134.8
134.4
135.4
137.3
135.4
141.8 '
137.7
151.5
140.9
133.5
133.5
137.6
2008
154.3
154.1
171.1
173.6
170.4
188.9
201.4
227.6
251.3
258.1
252.1
293.7
208.1
2009
294.8
289.7
295.0
285.2
282.0
277.8
276.4
261.2
263.6
264.9
264.5
260.9
276.3
2010
249.5
250.9
250.2
253.5
254.0
252.3
250.1
249.6
251.6
249.8
259.5
256.0
252.2
2011
262.9
269.8
268.3
272.7
275.3
276.8
274.9(P)
276.8(P)
278.3(P)
280.8(P)
P : Preliminary. All indexes are subject to revision four months after original publication.
4
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http://data.bls.gov/cgi-bin/dsry 12/12/2011
c
Town of Mayodan
NPDES Permit NC0021873
SLUDGE MANAGEMENT PLAN
The Town of Mayodan WWTP thickens sludge in one of two gravity thickeners and then it is
digested in an aerobic digester with the capacity of 0.4 MGD. The stabilized sludge is then land
applied either as a liquid directly from the digester or it may be dewatered on one of the 10 sand
drying beds and then land applied. The Land Application Permit (WQ0002672), permits a total
of 197.6 acres.
Town of Mayodan
NPDES Permit NC0021873
Present Operating Status
The Town of Mayodan Wastewater Treatment Plant is a 3.0 MGD design capacity facility. The
facility treats a combination of domestic and commercial wastewaters. The current treatment
scheme includes a mechanical bar screen, grit removal system, activated sludge and secondary
clarification. The treated effluent is disinfected by chlorination followed by a dechlorination
through the use of Sulfur Dioxide. Following is a schematic of the existing wastewater treatment
plant. The volumetric capacities are noted on the schematic.
ATTACHMENT II
SCHEMATIC AND BRIEF NARRITIVE
The Town of Mayodan Wastewater Treatment Plant is a 4.5 MGD design capacity facility. The
facility treats a combination of domestic, industrial, and commercial wastewaters. The current
treatment scheme includes a mechanical bar screen, grit removal system, activated sludge and
secondary clarification. The treated effluent is disinfected by chlorination followed by
dechlorination through the use of sulfur dioxide.
—I#ent Bar
been
In uent
Pump
Station
Infiu
from Unifi
Aeratio i Basins
1.25 MGD Total
Clarifier
I.0.143 MG
co
Sludge
Pumping
BuJding
Control
Building
Waste. Sludge .. . .
Return Sludge
Clarifier
0.143 MG
SO2
Bldg
Sludge
Thickeners
Flow
Meter
4
(Digestor
0.400 MG
4--
Cl2
SO2
Waste Sludge —Bldg-
Chlorine
Contact # 3
Aeration Basin
1.75 MGD
4-
Chlorine
Contact # 2
-*
Aeration Basin
1.5 MGD
Clarifier
0.400 MG
Clarifier
0.400 MG
Digestor
0.400 MG